/by Robert F. Van Dolah ... [et al.]. Van Dolah, Robert F. Charleston:Marine Resources Center, South Carolina Wildlife and Marine Resources Dept.,1979. Dredging Environmental aspects South Carolina Sewee Bay. Dredge spoil South Carolina Sewee Bay. Benthos South Carolina Sewee Bay. Estuarine ecology South Carolina Sewee Bay. GC 1000 .S6 no. 39 0-1 I Swawwl Effects of Dredg 'S n Unconfl ed,.,,.,. D lredgpd@, en thic' am in Sewee-:.',@ Risk, Van Do I a h $-Do, Da umes,' F" GC 1000 ja .D65 E34 1979 EFFECTS OF DREDGING AND UNCONFINED DISPOSAL OF DREDGED MATERIAL ON MACROBENTHIC COMMUNITIES IN SEWEE BAY, SOUTH CAROLINA' by Robert F. Van Dolah Dale R. Calder David M. Knott Magdalene S. Maclin Marine Resources Center South Carolina Wildlife and Marine Resources Department Charleston, South Carolina 29412 00 vs. Technical Report No. 39 091 1,0 ND South Carolina Marine Resources Center ill - 250 April 1979 Property of CSC Libraz7 Study funded under contract (#DACW-60-77-C-0013) for the U. S. Army Corps of Engineers, Charleston District. 4. t"05-0:-, 13 1w - Ca C" US Department of Commerce <=;, NOAA Coactal Services Center Library 2234 South Hobson Avenue CY1.1) Charleston, SC 29405-2413 =-5 TABLE OF CONTENTS Page LIST OF FIGURES LIST OF TABLES INTRODUCTION DESCRIPTION OF STUDY AREA METHODS Benthic Sampling .................................................................................... 1 Benthic Analytical Techniques ....................................................................... 1 Water Chemistry ..................................................................................... 3 RESULTS AND DISCUSSION 3 Water Chemistry ..................................................................................... 3 Benthic Oyster Dredge Collections ................................................................... 4 Benthic Grab Collections ............................................................................ 4 CONCLUSIONS .............................................................................................. 7 RECOMMENDATIONS 8 ACKNOWLEDGMENTS 8 LITERATURE CITED ......................................................................................... 9 LIST OF FIGURES Figure Page 1. Map of Sewee Bay disposal areas and station locations .............................................. 2 2. Bray-Curtis analysis of Sewee Bay benthic grab collections ......................................... 6 LIST OF TABLES Table Page 1. Hydrographic data collected at subtidal stations in the Sewee Bay area, South Carolina ........... 10 2-14. Occurrence of epifaunal invertebrates i n dredge collections from Sewee Bay stations .............. 12-30 15-32. Macroinvertebrate species collected from the Sewee Bay stations using the Ponar grab ............. 31-51 33. Species diversity, evenness and richness values for Sewee Bay grab samples from August 1977 to August-1978 ................................................................................... 52 34. Mean abundance and total number of species collected in the Sewee Bay grab samples from August 1977 to August 1978 ....................................................................... 53 35. Wet-weight biomass of Sewee Bay grab samples from August 1977 to August 1978 ..................... 54 small boats to navigate through the bay. Water INTRODUCTION currents are moderately strong in the area and re- sult from tidal action. Mean tidal range for Sewee Shoaling occurs at a number of locations in the Bay is 5.0 feet (National Ocean Survey, 1978). Atlantic Intracoastal Waterway (ATWW) through South Carolina, and periodic maintenance dredging is The disposal sites used in Sewee Bay during necessary to keep waterway channels at their pre- this study were intertidal mud flats adjacent to scribed depth. Materials dredged from most shoals the AIWW but separated from it by several small in the waterway through this state are usually barrier islands (Fig. 1). This area has infrequent- placed in diked disposal areas. However, a shoal ly received dredged material in the past, with the through Sewee Bay, requiring maintenance dredging last dredging operation occurring in 1964. However, in the winter of 1977-1978, has no confined dispo- no impact studies have been conducted in connection sal site nearby. An agreement was made during the with previous dredging operations in this area. annual waterway dredging consultation between the Corps of Engineers and several state and federal METHODS agencies in 1977 to undertake unconfined disposal of dredged material in the area. Benthic SampiiR& The impact of dredging and disposal of dredged Benthic samples were collected at 18 stations material in marine and estuarine environments has in Sewee Bay during the period from August 1977 to received increased attention in recent years (for September 1978. Four of the stations were located reviews, see Sherk, 1971; Saila, et al., 1972; in the dredged area of the waterway, two in peri- Windom, 1976; Morton, 1977), butThe@ reported pheral areas near Moores Landing, and 12 in a series effects of such activities on benthic communities of 4 transects at various distances from the dispo- are inconsistent. For example, Leathem, et al. sal sites (Fig. 1). All stations were sampled prior (1973), Slotta, et al. (1973) and Stickney and to dredging to provide base line data. Samples were Perlmutter (1975TA-served only minimal or short then collected at every station within two weeks term effects from dredging operations while Breuer after dredging to define the area and extent of (1962), Taylor and Saloman (1968), and Kaplan, et impact. The stations were again sampled three and al. (1974) noted more severe and long-term disrup- six months after dredging to monitor subsequent tion of benthic communities resulting from dredging recovery of the fauna. activities. In addition, other studies have noted graded effects of dredging and disposal operations Qualitative samples were collected at the 13 on benthic communities which were dependent on dis- subtidal stations using a modified oyster dredge, tance from the disposal sites and depth of the towed for three minutes. The dredge used during resultant sediment layer (Howell and Shelton, 1970; this study consisted of a rectangular steel frame Saila, et al., 1972; Maurer, et al., 1974; Bingham, measuring 53 em across the mouth, with a 1 m long 1978). bag of 3 cm stretch mesh polypropylene. A skirt of interlacing metal rings protected the bottom of the Due to the variable findings noted above and bag from chafing. After preliminary sorting of the the paucity of dredge-impact studies in areas dredge catch on station, unidentified epifaunal similar to Sewee Bay, the Division of Marine invertebrates and a representative sample of firm Resources of the South Carolina Wildlife and substrates were preserved in a 10% seawater-formal- Marine Resources Department entered into a contract dehyde solution and returned to the laboratory for with the Charleston District of the U. S. Army microscopic examination. Corps of Engineers to assess the effects of uncon- fined disposal of dredged material in this area. Quantitative samples were collected at all 18 The purpose of the study was to determine whether stations using a 0.05 m2 Ponar grab, Three repli- this method could be utilized with minimal distur- cate samples were taken at each station. After bance to the biological communities present and measuring the volume of each sample, the material possibly with less disturbance than would be caused was placed in large buckets and returned to the by diking new areas. laboratory where it was immediately washed through a 1.0 mm sieve. Organisms and sediment remaining STUDY AREA on the sieve after washing were preserved in a 10% seawater-formaldehyde solution and stained with Sewee Bay is a very shallow water mass located rose bengal to facilitate further sorting under west of Bulls Bay about midway along the coast of magnification. After identification and enumera- South Carolina. It is sheltered from the open tion, all animals were blotted dry to remove excess Atlantic Ocean by Bulls Island. The bay is border- liquid and weighed on a mettler model PN323 balance ed on the west by a series of small islands and to determine wet-weight biomass. bars, created from dredged material left during the original dredging of the Atlantic Intracoastal Sediment samples were also collected from each Waterway through the area. Spartina marshes station throughout the study. However, the results surround the bay to the south, east, and north. will not be presented in this report since signifi- The AIWW through the Sewee Bay area requires dredg- cant changes in sediment composition were never ing every 10 to 14 years to maintain a channel noted (Van Dolah,et al., 1979). depth of about 4 m. Benthic Analytical Techniques Although Sewee Bay appears to be relatively open at high tide, a substantial portion of its Community structure was analyzed using several area is exposed as mud flats and oysters bars at equations from information theory. Species diver- low tide. A number of channels, accessible either sity was measured with Shannon's formula (Pielou, from the AIWW or from creeks entering via Bulls 1975): Bay to the east, are deep enough (1-3 m) to permit H' = _ZP' 1092 P' :i! Ni'z. 4 :14'. A ve S77/70 f S U) co It 4. U) It 1% U 41 ca It ca tin C@4 Bill". p d t .:wa Imp, '11110"1 1, PQ It K'a till 41 1111 11 Q) MO. IIIIIIJIV, III III rs 11 1 11-3111 11, VII, I' P. 1111111111 C@! LL 11111' U) c w '0 - . . . . . . I ... ... It... 0 44 lot." till 11 0 1111111 At'. ca U) LI , I'l Z bill 2 to 4 . F " ca 0 U) - II Jill, I Ilk 0 it 0 IF 4 V.- rX4 w 1 4 A, where H' is the diversity in bits of information per 224F (APHA, 1971). individual, and pi equals-a-1 or the proportion of N . the sample belonging to the ith species. Species RESULTS and DISCUSSION richness was calculated using the formula: S-1 Water Chemistry: SR = InN where S is the number of species and 1nN is the Temperature - The shallow waters of Sewee Bay natural logarithm of the total number of individuals rapidly reflected variations in air temperature; of all species in the sample. Evenness or equita- wide seasonal differences were observed during this bility, the distribution of individuals among the investigation (Table 1). Temperatures were low various species, was measured by: (< 7.0 OC) throughout the study area in January as H' S7outh Carolina experienced an unusually cold winter. J' = 1092S Temperatures of approximately 20 'C by late April where H' is the species diversity in bits of infor- and 30 OC by late July were observed in 1978. A mation per individual and S is the number of species. maximum temperature range of 27.3 OC (from a January reading of 4.7 OC at SB07 to 32.0 OC at SB03 in Faunal homogeneity was measured from both July) was noted during the study. Differences from qualitative dredge samples and quantitative grab station to station were relatively minor on any samples. The qualitative measure of similarity given sampling date, and differences between surface used was the Sorensen coefficient (Sorensen, 1948): and bottom readings were never large (a maximum of 2C 1.8 OC at SBOl in April). Thus, waters of Sewee Sl = (a+b) Bay are well-mixed with respect to temperature. where a and b are the numbers of species obtained at a station on each of the two collection dates and c Salinity - Although Sewee Bay is influenced to some is the number common to both. The quantitative extent by the AIWW, it is relatively isolated from measure of similarity was the Bray-Curtis coefficient any major sources of fresh water other than rainfall (Boesch, 1977): and runoff from adjacent land areas. Salinity measurements taken during the study were all in the 2imin(xii,xii) euhaline range (30-40 O/oo), and fluctuations were S2 = E relatively minor (Table 1). Salinities were highest i(xij+y-ik) in summer and autumn samples and lowest in winter. where xij and xik are the number of individuals of Differences in salinity measurements from surface the i th species in two collections under comparison. to bottom and from station to station on a given Using this coefficient, a normal analysis was com- date were negligible. As Sewee Bay has high and pleted on modified data sets with a flexible sorting stable salinities with no distinct halocline in any strategy and standard BETA value of -0.025. All direction, it corresponds with the characteristics data were log transformed and species which occurred of a neutral embayment. According to Glooschenko in fewer than 4 collections were eliminated from the and Harriss (1974), a neutral embayment is defined analysis. However, prior to this elimination, as a partially-enclosed marine environment receiving certain species were grouped together to reduce negligible fresh water inflow from rivers and with error from incomplete identification of damaged precipitation approximating evaporation. specimens. These groups are as follows: Pinnixa Glooschenko and Harriss considered water temperature, sayana were lumped with Pinnixa sp.; Panopeus light, and nutrients to be the primary factors of herbstii with Xanthidae (undet.); Squilla empusa ecological importance in temperate neutral embayments. with Stomatopoda (undet.); Notomastus lobatus with Certainly, stresses due to variable salinity on Notomastus sp.; Scoloplos a with Scoloplos sp.; marine organisms in Sewee Bay are relatively small, Haploscoloplos robustus, H. foliosus and H. at least for species occurring subtidally. Although fragilis with Haploscoloplos sp.; Nemertina sp. A it is possible that salinities of the area may be with Nemertina (undet.). These groupings make reduced somewhat following heavy rainfall, no the similarity comparison between collections more indication of this was evident from the present meaningful since, with few exceptions, the specimens study. which could only be partially identified were probably the species which could be identified. Dissolved Oxygen - Oxygen levels were never observed to be critically low in Sewee Bay during the study Water Chemistry period (Table 1). Dissolved oxygen values ranged from a low of 5.0 mg/l in bottom samples from stations Water chemistry was monitored throughout the SBO8, SB17, and SB18 during summer to a high of study using Van Dorn bottles (6-liter capacity) at 10.9 mg/l in surface samples from SB08 and SB10 in every station in Sewee Bay except SB02, SB04, SB09, January. Oxygen readings were lowest in summer, SBll and SB16. Samples were collected 1 m below the highest in winter, and intermediate in spring and water surface and 0.3 m above the bottom at each autumn. The winter samples, collected within a few station. Parameters measured included temperature, days after dredging and unconfined disposal of dissolved oxygen, salinity, turbidity, and total dredged material, indicate that the dredging opera- and settleable solids. Water temperatures were tion was not followed by a widespread and drastic measured when the samples were collected using reduction in dissolved oxygen levels. Dissolved thermometers mounted in the Van Dorn bottles. oxygen levels could not be recorded for samples Dissolved oxygen and turbidity samples were fixed taken immediately after dredging at station SB04 due immediately after collection. In the laboratory, to very high silt levels. However, the epibenthic dissolved oxygen was analyzed by the modified sample collected shortly thereafter smelled noxious, Winkler titration method. Turbidity and salinity which may have been attributable either to anaerobic were measured using a Hach Model 2100A Turbidi- conditions, or smothering and subsequent decomposi- meter and a Beckman Model RS7B Induction Salino- tion of some bottom-dwelling organisms. meter. Solids were analyzed by American Public Health Association (APHA) Standard Methods 224C and The low oxygen values observed in summer are due 3 to a combination of factors, including high water Oyster dredge samples were taken at four temperatures and the respiration of organisms. stations (SB03, SB07, SB12, SB17) along the axis However, D.O. levels never departed significantly of Sewee Bay (Fig. 1). Of these, SB03 was from saturation levels. The effects of dredging especially noteworthy because it had the richest would probably have been much more adverse had the assemblage of epifaunal species found anywhere operation been conducted at any other season of in Sewee Bay during the study. The bottom at this the year, but especially in summer when oxygen station consisted of relatively mud-free shell, levels are low and community metabolism is high. and an average of 43 species was collected over Waterway dredging through Sewee Bay was fortuitously the four sampling periods. While the minimum well-timed to coincide with a period when its number of species collected (32) came immediately environmental impact, particularly with respect after dredging, there was no evidence that the to D.O., was probably lowest. drop in species numbers could be attributed to smothering from spreading dredged material. Turbidity and Solids - Values for these parameters Instead, many of the epifaunal species found there, were rather high throughout the year in Sewee Bay. especially certain hydroids, entoprocts, and Pronounced increases as a result of dredging were sponges, undergo a period of dormancy in winter apparent in winter samples from four stations due to low water temperatures and were simply not (SBOI, SB03, SB04, SB05), while samples from the active during February. Species numbers and remaining stations at this time were generally community composition in spring and summer samples comparable to, or even lower than, those collected were very similar to those noted in the pre-dredge during other seasons of the year (Table 1). It is survey (Table 3). The bottom at station SB07 particularly noteworthy that samples from stations consisted largely of broken shell and mud, but a SBO1, SB03, SB04, and SB05 were taken within 4-5 moderately diverse faunal assemblage was present days after dredging and unconfined disposal of (Table 6). No adverse effects were apparent from dredged material in and adjacent to these sites, the disposal of dredged material nearby. Two other and while the dredge was still operating in the stations in the middle of Sewee Bay (SB12, SB17) waterway through Sewee Bay. Samples from the were located in muddy, shallow water areas. The remaining stations were collected shortly after epifauna at both stations, and particularly SB12, all dredging in the area had been completed. This was impoverished and no changes were detectable indicates that abnormally high levels of turbidity that were obviously related to disposal practices and solids resulting from the dredging operations (Tables 9, 13). were of very short duration. Several of the turbidity and solids values reached their lowest Four stations were also sampled at the mouths levels in winter. This corresponds with the data of creeks along the eastern edge of Sewee Bay of Mathews and Shealy (1978), who observed that (Fig. 1). The relatively low number of species turbidities and solids in the Edisto and Cooper observed in February samples at stations SB08, SB13, estuaries were lower in winter than at any other and SB18 was again attributed largely to the time of the year. seasonal dormancy of a number of sponges, hydroids, entoprocts, and others (Tables 7, 10, 14). Benthic Oyster Dredge Collections: However, the reduction in species numbers collected at station SB04 was drastic (Table 4), and clear A moderately diverse assemblage of species was evidence of smothering by sediments from unconfined noted in the epifauna of the Sewee Bay area. Over- disposal of dredged material was apparent at the all, species composition was relatively similar time of sampling. A considerable amount of soft from one location to another, especially before mud was taken in the February oyster dredge tow. dredging operations were undertaken (Tables 2-14). In addition, dead mud crabs and bivalves (Tagelus For example, a suite of relatively stenohaline plebeius, Tellina sp.) were collected and the bryozoans (Bugula neritina, Schizoporella errata, entire sample was malodorous. No appreciable Hippoporina verrilli, Microporella ciliata, recovery of the fauna was observed when sampling Parasmittina--nitida) was present at the majority was conducted in late April. By the summer of 1978, of the 13 stations where sampling with a modified the community was still less diverse than before oyster dredge was conducted. dredging but a substantial increase in the number of species had occurred over the winter and spring Physical disruption of epibenthic assemblages, samples, and faunal homogeneity had increased caused by dredging of the Atlantic Intracoastal markedly (Table 4). Waterway during January of 1978, was clearly evident in samples from stations SBOl. SB05, SBIO, Finally, oyster dredge collections were taken and SB15 (Tables 2, 5, 8, 12). The average number at station SB14 in a small creek west of the AIWW. of species at these four waterway stations was 28 This station was relatively isolated from disposal before dredging and 6 immediately after. Repopu- sites and no impact was observed on the epifauna lation was noted'in subsequent sampling intervals. of the area (Table 11). Three months after dredging, the average number of species at the four stations in the AIWW had risen Benthic Grab Collections: to 20. Six months after dredging, the average number of species was 22, only slightly lower than Species Composition - A total of 129 identifiable the number observed the previous summer. Faunal species was collected by the Ponar grab in Sewee homogeneity between pre-dredge and post-dredge Bay (Tables 15-32). Of these, four polychaete collections was low to moderately low immediately species, Lumbrineris tenuis, Paraprionospio pinnata, after dredging but increased substantially by the Heteromastus filiformis, and Nereis succinea, end of the study (Tables 2, 5, 8, 12). The total comprised over 46% of the total number of animals catch of animals and hard substrate was usually collected throughout the study period. These small both before and after dredging at all of the species, as well as several others, were quite stations in the waterway. ubiquitous in their distribution among stations. 4 For example, L. tenuis, H. filiformis and N. succinea of dredged material (Tables 20, 25, 30). All of these were present at all 18 stations at least once during stations were separated from the disposal sites by the study period while P. pinnata was observed at 17 short projections of land which may have deflected much stations during the one-year period. of the dredged sediments. Tn addition, many of the species at these stations have been categorized as The community structure of the channel stations pollution resistant (Wass, 1967; Saila, et al., 1972: (SBOl, SB05, SB10, SB15) was dominated by P. pinnata Maurer, et al., 1978) and could have surviv7ed the in the late summer prior to dredging. Oth@er abun- deposition which did occur. The Bray-Curtis coefficient dant species generally present at this time included analysis of these stations indicated that the species the decapod Ogyrides limicola and two polychaetes, composition was similar throughout the year at SB11, L. tenuis (all stations) and Glycinde solitaria and similar during the first three sampling quarters at (SId5). Following the winter dredging operation, SB06 (Fig. 2). The decline in community complexity and P. pinnata densities had decreased at all stations density during the fourth quarter sampling period at and, at two stations, it was replaced in terms of SB06 (Table 20) was probably not due to disposal effects numerical dominance by the pelecypod Mulinia as similar decreases were not observed in the third lateralis (SB05) and the decapod 0. limicola quarter sampling effort. At station SB16, community (SB10). structure was dissimilar throughout most of the study period (Fig. 2). However, it is unlikely that dredged An analysis of overall species composition material had much influence as a strong tidal current using the Bray-Curtis similarity coefficient showed was present and spoil deposits were never observed. no consistent or distinctive patterns among channel stations with respect to dredge effects. Six months The communities at stations located in the middle after dredging, species composition was only slightly of Sewee Bay (SB03, SB07, SB12, SB17) were not severely similar to the pre-dredge species composition at affected by spoil deposition. During the initial stations SBOI and SB05, and dissimilar at stations sampling period (August, 1977), the community at SB03 SB10 and SB15 (Fig. 2) even though these sampling was depauperate and dominated by L. tenuis. After periods were in equivalent seasons. However, spoil deposition, the community sampled was much more comparable trends were observed at stations which complex (Table 17) and remained diverse throughout the should not have been affected by the dredging rest of the study period, although species composition operation (discussed later). Thus, some of the was dissimilar on each sampling date (Fig. 2). Para- changes in community structure may have been due prionospio pinnata, which was present at the last three to normal seasonal and sampling variations. sampling quarters, may have been introduced to the community through deposition as it was not present in Alterations in species composition which the first quarter. Stations SB07, SB12 and SB17 showed might be attributable to the dredging operation trends similar to SB03 although initial community were noted at station SBOl. Three months after structure was more complex. Spoil deposits were present dredging, there was a substantial increase in at SB17 in the second and third sampling quarters and the number of species normally associated with may account for some of the changes observed (Fig. 2). "live" bottom communities at this station (Table However, sediment characteristics were not visibly 15). Therefore, it is possible that the dredge altered at SB07 and SB12, and community structure was removed soft mud from the channel down to a firmer different during equivalent seasons at SB12 but similar substrate which permitted a "live" bottom community at SB07 (Fig. 2). Therefore, it is likely that much of to form. However, this community is either patchy the variation in species composition at all of these or was smothered by channel wall slump since a stations is due to a combination of seasonal effects similar species composition was not observed during and sampling variability resulting from patchy community the fourth quarter sampling period. distribution. Community structure at stations nearest the Stations farthest from the disposal sites (SB04, disposal sites exhibited varied effects from SB08, SB13, and SB18) also showed changes in community deposition of dredged material. Station SB02 structure immediately after, and three months after, was situated very close to a disposal site and deposition of dredged material. Soft, oozy sediments was the most severely affected. Prior to dredging, were present at stations SB04, SB08, and SB18 on these the community at this station was dominated by the sampling dates and probably accounted for some of the polychaetes L. tenuis and Aricidea fragilis changes observed. For example, P. pinnata was a (Table 16). Dwr-ing the se_condquar@tersampling dominant species at two of these stations immediately period, the dominant species was H. filiformis, after deposition, although it was not present before. but L. tenuis remained an important component of As this species was common in the channel prior to the community. Most of the changes which occurred dredging, it may have been introduced with the spoil. at this time were probably seasonal,as dredged However, it is unlikely that spoil disposal severely material was still being deposited nearby. Three influenced the communities through smothering since a months after spoil deposition, however, the diverse assemblage of species was always present. Six community was reduced to one infaunal species, months after dredging, the species composition at these N. succinea (a spoil-resistant polychaete; stations was slightly similar to pre-dredge species Iffaurer, et al., 1978) and two epifaunal crustacean composition (Fig. 2). The community structure at SB13, species (each represented by one individual). on the other hand, was dissimilar on every sampling Thus, the original community was smothered and date (Fig. 2). Even so, no decline in community although community complexity had increased to a complexity at SB13 occurred as a result of spoil pre-dredge level six months after dredged material deposition. deposition, the species composition was altered (Table 16) and dissimilar by Bray-Curtis Two stations which were not influenced by the similarity coefficient analysis (Fig. 2). dredging operation were SB09 and SB14. Both of these stations were out of the channel and on the opposite side Stations SB06, SB11, and SB16, on the other of the waterway with respect to the disposal sites. Thus, hand, were not noticeably affected by deposition changes which occurred at these stations were most likely 5 Figure 2. Bray-Curtis analysis of the Sewee Bay benthic grab collections. First Quarter = samples collected before dredging; Second Quarter samples collected immediately after dredging; Third Quarter samples collected 3 months after dredging; Fourth Quarter = samples collected 6 months after dredging and 1 year after first quarter samples. SIMILARITY .8 .6 .4 .2 0 -.2 -.4 -.6 STATION(OUMTER) 1(1) : 00) 5 (1) 90) 140) 13(4) A 1? (2) 40) 3(4) 50) 1514) - - - - - - - 4 OW B 1 (4) 5(4) 10(2) 5 C 5(3) - - _13 D I W14 --I 5L - - - - - - - - - 2. ?41 4(2) E 6(4) _17,it4) - - - - - - - - - 14(3) 13(3) 18(3) 4(3) 170) 3(3) 8(3)- 16(3) F 6(2) 9(2) 12(3) 9(3) 100) 18(2) 8(2) ? (2) 1(3) 170) G 7(4) 18(4) 30 - - - - - - - - - - - - - 14-T4) 2(2) 12(1) 6(3) 60) H 16(l) G(2) 30) 130) 20) 9A -19 ) - IU(4) - - - - - - 11(3) 1(1) 1000 12(,Q 110 9@=7 - - - - 12-0 2(3)- .8 .6 .4 .2 0 -2 -.4 -.6 SIMILARITY 6 due to seasonal effects. Station SB09 was domin- the rest of the study period. The observed increase ated by L. tenuis throughout the study period was the result of increases in both evenness and except in January (second quarter) when M. species richness. H' values fluctuated at stations lateralis was the dominant species (Table 23). SB04 and SB08 and had declined to relatively low Sporadic increases in M. lateralis densities values by the fourth qjjarter sampling period due to at this time of the year have also been noted decreased evenness and species richness. H' values in previous studies (Boesch, 1973; Stickney and at SB09 remained similar throughout this study Perlmutter, 1975). The community structure at although species richness did increase during the SB14 was variable, partly due to seasonal effects. winter and spring months. However, this station had an extremely hard bottom with strong currents present, and much of the Abundance - An analysis of the mean abundance of variability is attributable to poor grab samples. the benthic communities at each station (Table 34) At both stations, the community was similar in the indicated that the dredging operation had some second and third quarters but dissimilar in the short term, localized effects in Sewee Bay. As first and fourth quarters (Fig. 2). expected, mean densities at all channel stations (SBO1, SB05, SB10, SB15) declined immediately after Species Diversity -The analysis of species dredging, whereas densities had increased during diversity (H'), evenness (J') and species richness this period at most of the stations farthest from (SR) of benthic communities in Sewee Bay did not the dredging activity (SB04, SBO8, SB09, SB14, SB18). reflect any widespread changes resulting from the The percent of decrease at the channel stations dredging operation (Table 33). varied, ranging from a minimum of 49% at SB10 to a maximum of 85.2% at SB15. However, declines in H' values increased immediately after dredg- abundance were only significant (P<0.05 ANOVA test) ing at two of the channel stations (SB05, SB15) at three of the channel stations (SB05, SB10, SB15) and all channel stations had higher H' values and, at all but one station (SB15), abundance had three months after the dredge had passed through increased to pre-dredge levels by April. the area. This increase was primarily due to increased species richness and evenness at Significant density changes (P<.05, ANOVA test) stations SBO1, SB10 and SB15 and increased were also observed at two other stations. The evenness at station SB05. Six months after community at station SB16 increased during the dredging, H' had decreased at all channel second quarter sampling period, and the community stations to values which were approximately at station SB17 decreased in abundance during the equivalent to those observed in the first quarter fourth quarter sampling period. These changes were sampling period. probably due to seasonal effects or sampling varia- bility as discussed previously. Fluctuations in Species diversity patterns were more varied mean densities at all other stations were not signi- at stations nearest the disposal sites. The ficant during the study period (P>.05, ANOVA test). communities at all of these stations (SB02, SB06, SB11, SB16) were more diverse immediately after Biomass - Wet-weight biomass estimates (Table 35) dredged material disposal when compared with the varied from a low of 0.06 gms at stations SB02 and pre-dredge, August sampling period. H' values SB03 (August 1977, 1978) to a high of 7.02 gms at continued to increase at station SBll and SB16 station SB15 (August, 1977) with no significant during the third quarter sampling period before patterns discernable. The observed variability is declining to values approaching those observed due to (1) the low biomass present at these stations initially. H' values at station SB06 remained on any sampling date, (2) high variability between the same throughout the year with the exception replicate samples, and (3) the occasional presence of the increase noted in January. Diversity of large bivalves, gastropods, anemones, etc. in the values for station SB02, on the other hand, samples. The effects of these factors are best reflected the demise of this community through exemplified by an analysis of two stations. Pre- smothering as H', V and SR values were quite vious data indicated that SB02 was the most severely low three months after spoil deposition. affected station in Sewee Bay through smothering However, by the end of the study period, all from deposition of dredged material which resulted three indices had increased at station SB02 to in a substantial decline in community complexity and values higher than those observed prior to the diversity by April, 1978. However, by April biomass dredging operation. had increased to the highest values observed due to the presence of several relatively large N. succinea. Species diversity (H') was consistently The community at station SB14, on the ot band, higher after spoil deposition at all of the was not significantly influenced by the dredging stations located in the middle of Sewee Bay operation because of its location. Nonetheless, (SB03, SB07, Shl2) except station SB17. This biomass decreased from a high initial value of 2.89 was primarily due to increased species richness. gms in August, 1977 to a low of 0.27 gms by April, At station SB17, H' values also increased in 1978. Thus, it is difficult to interpret changes January but later declined to very low values in biomass with respect to effects of dredging and by the end of this study. These values are disposal of dredged material. probably an artifact of sampling variability, however, as similar values should have been observed in April if deposition of dredged CONCLUSIONS material was the cause for this decline. In summary, the effects of dredging and uncon- fined disposal of dredged material on epifaunal Diversity values varied at the stations macroinvertebrate communities were detectable at farthest from the disposal sites. H' increased five of the 13 stations sampled with an oyster dredge at stations SB13, SB14 and SB18 after the dredg- in Sewee Bay. Disruption of the epibenthos by ing operation, and remained higher throughout channel dredging was apparent at each of the four 7 stations located in the AIWW. However, the epi- the area. fauna was not especially rich at any of these four stations before dredging, and faunal composition 2) Good flushing patterns present at many Sewee at the end of the study approached that observed Bay stations, as well as flow diversion by land and during the baseline survey conducted in the summer oyster hummocks which protected other areas where of 1977. Of the eight stations in Sewee Bay proper stations were located. where dredge tows were made, a severe impact on the benthos was noted only at SB04. Evidently, dredged 3) The presence of species at several stations material from the disposal area was carried by that are resistant to spoil deposition or unhealthy water currents into the creek where SB04 was located. conditions. Some recovery was noted at this station six months after dredging. Species numbers were generally 4) The presence of several ubiquitous species lower at all stations in the winter after dredging in Sewee Bay, permitting rapid recolonization in when compared with samples collected during the areas which were affected. summer. This was attributed largely to normal seasonal differences in community composition. The 5) The similarity of sediment composition wide annual range of water temperature influenced present in the channel and disposal areas of Sewee the activity patterns of several epifaunal species. Bay. A number of sponges, hydroids, entoprocts, and ascidians were observed in a dormant state during 6) Seasonal effects, which minimized adverse the winter sampling period. These species returned water quality conditions during the winter dredging to activity with the return of warmer water tempera- period, and caused increased community diversity at tures in spring. most stations afterwards; thereby countering dredge and disposal effects. The effects of dredging on the infaunal commun- ities in Sewee Bay were short term and localized. RECOMMENDATIONS Immediately after dredging, the community structure at most channel stations was different when compared Disposal of dredged material can be managed to with pre-dredge samples. Total animal abundance and minimize adverse effects in the estuarine environment. biomass had also decreased. Although some of these Depending upon the timing and frequency of disturbance, changes are due to seasonal effects, dredging Rhoads, et al. (1978) suggested that the productivity obviously affected the channel communities through of benttd-c -communities could actually be enhanced by bottom disturbance. However, this disruption did dredge-spoil disposal operations. Although the not adversely affect species diversity which in- following recommendations may not enhance benthic creased after dredging due to a decline in P. pinnata productivity, adverse effects should be minimized dominance, and a concomitant increase in species in Sewee Bay if: richness. Six months after the dredge had passed .through the area, all stations showed indications of 1) Dredging and disposal of dredged material returning to pre-dredge conditions. The lack of any are undertaken in late fall and/or early winter to long term, adverse effects in the channel correlates reduce adverse effects on recruitment patterns. well with studies on the intracoastal waterway in Georgia (Stickney and Perlmutter, 1975) and in 2) Dredging operations are conducted relatively Delaware Bay (Maurer, et al., 1974). often, so that the volume of dredged material is not large at any given time. The effects of unconfined disposal on the in- fauna in Sewee Bay were varied and somewhat depen- 3) The practice of using several disposal sites dent on distance from the points of deposition. is continued in any future operations. The intertidal station, SB02, was the most severely affected through smothering which altered community ACKNOWLEDGMENTS structure and decreased species diversity, but did not affect community biomass and numerical abundance. We are greatly indebted to a number of our co- Other stations in close proximity to the disposal workers who assisted us during the study. Mary Jo sites did not appear to be adversely affected by Clise, Rachel Goldberg, Paula Keener, Priscilla deposition. The community composition at stations Knight, Parker Lumpkin, Kathleen Meuli, Todd Nimmich, further from the spoil sites changed during the Rick Richter, and James Scoggin were particularly study period, but many changes observed were due helpful in various aspects of the field work. to normal seasonal variability. Thanks are due to W. Z. Carson, Rob Dunlap, and Don Marchette for allowing us to use their boats. In conclusion, the influence of dredging Water chemistry samples were analyzed by Kathy operations on benthic communities in Sewee Bay were Austin and Virginia Young. Dr. E. L. Bousfield short term and isolated. Furthermore, it is un- verified the identification of several amphipod likely that dredged material disposal had a profound species in our samples. We wish to thank John effect at any station in terms of the ecological Carothers, Robbin Blackman, and Steve Morrison of interactions of benthic communities with higher the Charleston District, U. S. Army Corps of trophiclevels. These results differ from other Engineers, for their part in the study design and studies in which larger areas were noticeably for their encouragement and support of our work. smothered and subsequently recolonized (Saila, et Chris Brosseau, Nicky Kopacka, and Lourene Rigsbee al., 1972; Maurer, et al., 1974; Bingham, 1978). assisted in the processing of data. Mary Anne T-he absence of widespread, long-term effects in this Carson, Pat DuPree, and Lexa Ford typed the manu- study may be due to several factors. These include: script. M. H. Shealy, Jr. critically reviewed the manuscript. This study was supported under Contract 1) The use of several disposal sites in Sewee Number DACW60-77-C-0013 from the U. S. Army Corps Bay which spread dredged material more evenly over of Engineers, Charleston District. 8 Maurer, D. L., R. T. Keck, J. C. Tinsman, W. A. LITERATURE CITED Tinsman, W. A. Leathem, C. A. Wethe, M. Huntzinger, C. Lord, T. M. Church. 1978. American Public Health Association. 1971. Standard Vertical migration of benthos in simulated methods for the examination of water and waste- dredged material overburdens. Vol. 1: Marine water including bottom sediments and sludges. benthos. U. S. Army Engineer Waterways 13th ed. Amer. Public Health Assoc. Inc., New Experiment Station, Tech. Rept. D-78-35. 97 p. York, N. Y. 769 p. Morton, J. W. 1977. Ecological effects of dredging Bingham, C. R. 1978. Aquatic disposal field inves- and dredge spoil disposal: A literature review. tigations Duwamish waterway disposal site Puget Technical Paper #94, U. S. Fish and Wildlife Sound, Washington. Appendix G: Benthic Service. 33 p. community structural changes resulting from dredged material disposal Elliott Bay disposal Pielou, E. C. 1975. Ecological diversity. Wiley- site. U. S. Army Engineer Waterways Experiment Interscience, New York. 165 p. Station, Tech. Rept. D-77-24. 103 p. Rhoads, D. C., P. L. McCall, and J. Y. Yingst. Boesch, D. 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R. macrobenthos of the Edisto and Santee River Hancock, J. E. McCauley, and R. Parr. 1973. systems, South Carolina. South Carolina Mar. Effects of hopper dredging and in channel Res. Center Tech. Rep. No. 22. 50 p. spoiling in Coos Bay, Oregon. Oregon State Glooschenko, W. A., and R. C. Harriss. 1974. Univ., Corvallis. 141 pp. Neutral embayments. Pages 488-497. In Sorensen, T. A. 1978. A method of establishing H. T. Odum, B. J. Copeland, and E. A. McMahan groups of equal amplitude in plant sociology (eds.), Coastal ecological systems of the based on similarity of species content and its United States, Vol. I. The Conservation application to analyses of the vegetation on Foundation, Washington, D. C. Danis commons. K. dan5ke Vidensk. Selsk. Biol. Howell, B. R. and R. G. J. Shelton. 1970. The Skr. 5(4): 1-34. effect of china clay on the bottom fauna of Stickney, R. R., and D. Perlmutter. 1975. Impact St. Amstell and Mevagissy Bays. Jour. Mar. of intracoastal waterway maintenance dredging Biol. Ass. U.K. 50: 593-607. on a mud bottom bentho5 community. Biol. Kaplan, E. H., J. R. Welker, and M. G. Kraus. Conserv. 7: 211-226. 1974. Some effects of dredging on popula- Taylor, J. L., and C. H. Saloman. 1968. Some tions of macrobenthic organisms. U. S. effects of hydraulic dredging and coastal Natl. Mar. Fish. Serv., Fish. Bull. development in Boca Ciaga Bay, Florida. U. S. 72(2): 445-480. Fish Wildl. Serv. Fish. Bull. 67(2): 213-241. Leathem, W., P. Kinner, D. Maurer, R. Biggs, Van Dolah, R. F., D. R. Calder, F. W. Stapor, Jr., and W. Treasure. 1973. Effects of spoil R. H. Dunlap, and C. R. Richter. 1979. disposal on benthic invertebrates. Mar. Atlantic intracoastal waterway environmental Pollut. Bull. 4(8)* 122-125. studies at Sewee Bay and North Edisto River. Mathews, T. D., and M. H. Shealy, Jr. 1978. Final Report, Contract #DACW-60-77-C-0013, Hydrography of South Carolina estuaries, Charleston District, U. S. Army, Corps of with emphasis on the North and South Edisto Engineers. 146 p. and Cooper Rivers. South Carolina Mar. Res. Wass, M. L. 1967. Biological and physiological Center Tech. Rep. No. 30. 148 p. basis of indicator organisms and communities: In: Olson, T. A. and F. J. Burgess, Pollution Maurer, D., R. Biggs, W. Leathem, P. Kinner, _i@n_d Marine Ecology, Interscience, N. Y. pp. 271- W. Treasure, M. Otley, L. Watling, and 283. V. Klemas. 1974. Effect of spoil dis- posal on benthic communities near the mouth Windom, H. L. 1976. Environmental aspects of of Delaware Bay. College of Marine Studies, dredging in the coastal zone. CRC Critical Univ. of Delaware, Lewes and Newark. 231 pp. Rev. in Environ. Control. 7: 91-109. 9 Table 1. Hydrographic data collected at subtidal stations in the Sewee Bay area, South Carolina. SOLIDS STATION TEMP. SALINITY D.O. TURBIDITY (mg/1) STATION DATE DEPTH DEPTH (C) ('/oo) (mg/1) (FTU) TOTAL SETTLEABLE SBOl 10-19-77 4 Surface 17.1 34.53 7.1 16.0 110.4 38.8 Bottom 16.9 34.58 7.4 19.0 110.4 80.8 1-17-78 Surface 7.0 30.62 9.2 14.0 - - Bottom 6.9 31.89 9.4 .68.0 189.2 39.2 4-24-78 Surface 20.9 32.94 7.3 9.0 96.8 13.2 Bottom 19.1 32.94 6.9 26.0 165.6 28.0 7-24-78 Surface 30.2 34.10 5.6 12.0 103.2 76.4 Bottom 30.1 34.15 5.8 17.0 137.2 75.6 SB03 1110-18-77 1 Surface 16.6 34.66 7.3 12.0 104.4 28.0 Bottom 16.5 34.73 7.6 12.0 126.8 28.4 1-17-78 Surface 6.9 32.01 9.4 30.0 131.2 30.4 Bottom 6.9 32.09 9.5 44.0 179.2 80.0 4-24-78 Surface 19.0 32.98 7.0 21.0 - - Bottom 19.0 32.89 6.9 19.0 - - 7-24-78 Surface 32.0 34.07 5.5 16.0 120.4 31.6 Bottom 32.0 34.07 5.6 18.0 138.0 41.6 SB04 10-18-77 3 Surface 16.8 34.69 7.7 11.0 101.2 30.4 Bottom 16.8 34.74 7.7 34.0 106.4 24.8 1-17-78 Surface 6.5 32.07 9.6 34.0 134.4 56.0 Bottom 6.4 4-24-78 Surface 20.1 32.98 7.2 12.0 103.6 10.4 Bottom 19.8 33.00 7.2 16.0 131.6 14.4 7-24-78 Surface 29.9 34.00 5.4 20.0 127.6 60.8 Bottom 29.9 34.02 5.2 21.0 86.8 21.2 SB05 10-19-77 4 Surface 17.4 34.31 7.2 12.0 115.2 30.4 Bottom 16.9 35.48 7.2 17.0 - - 1-17-78 Surface 6.9 32.16 9.7 23.0 154.8 58.8 Bottom 6.7 32.09 9.7 45.0 - - 4-24-78 Surface 20.3 32.99 7.2 7.5 - - Bottom 20.1 33.00 6.9 15.0 - - 7-24-78 Surface 29.8 34.31 5.6 11.0 - - Bottom 29.5 34.31 5.2 18.0 121.2 30.0 SB07 10-18-77 2 Surface 16.6 34.61 7.5 8.9 108.8 36.0 Bottom 16.5 34.58 7.5 11.0 121.6 40.8 2-1-78 Surface 4.8 30.57 10.7 16.0 82.0 2.4 Bottom 4.7 30.62 - 17.0 77.0 1.8 4-24-78 Surface 19.7 32.97 6.9 13.0 116.0 19.2 Bottom 19.7 33.02 6.9 13.0 135.6 10.4 7-24-78 Surface 29.8 34.26 5.5 15.0 138.4 19.6 Bottom 29.8 34.30 5.5 19.0 107.6 29.6 SB08 10-18-77 2 Surface 16.5 34.61 7.6 14.0 117.2 21.2 Bottom 16.5 34.61 7.8 15.0 134.4 9.2 2-1-78 Surface 4.9 30.62 10.9 18.0 88.0 25.2 Bottom 5.0 30.60 10.7 17.0 96.0 34.4 4-24-78 Surface 20.0 32.90 6.9 17.0 - - Bottom 20.0 33.01 6.9 19.0 160.0 27.6 7-24-78 Surface 30.0 34.03 5.1 21.0 150.0 43.2 Bottom 30.0 34.05 5.0 24.0 147.2 2.0 SB10 8-22-77 4 Surface 27.4 33.66 6.4 12.0 - Bottom 27.0 33.62 6.1 38.0 139.2 18.0 2-1-78 Surface 4.9 30.87 io.9 11.0 66.4 Bottom 5.0 30.88 10.7 12.0 77.2 6.8 4-24-78 Surface 20.9 33.01 7.8 18.0 125.6 38.4 Bottom 19.8 33.06 6.9 22.0 154.8 18.0 7-24-78 Surface 30.3 34.38 5.5 17.0 132.8 62.8 Bottom 29.3 34.35 5.,6 10.0 115.6 51.6 10 Table 1. (Cont.) SOLIDS STATION TEMP. SALINITY D.O. TURBIDITY STATION DATE DEPTH DEPTH (C) (0/00) (mg/1) (FTU) TOTAL SETTLEABLE SB12 10-19-77 1 Surface 14.9 34.77 7.2 19.0 109.6 15.2 Bottom 14.9 34.71 7.4 23.0 - - 2-1-78 Surface 4.9 30.61 10.6 21.0 124.8 33.2 Bottom 4.9 30.65 10.4 22.0 163.2 77.2 4-25-78 Surface 21.9 33.14 7.2 17.0 114.8 47.6 Bottom 21.9 33.15 6.9 64.0 232.0 58.4 7-24-78 Surface 30.0 34.18 5.5 14.0 - - Bottom 29.9 34.18 5.5 20.0 105.6 13.6 SB13 10-19-77 3 Surface 16.6 34.60 7.2 13.0 - - Bottom 16.5 34.60 7.5 12.0 - - 2-1-78 Surface 5.0 30.53 10.7 16.0 - - Bottom 4.8 30.57 10.6 21.0 - - 4-24-78 Surface 21.0 33.04 7.2 24.0 - - Bottom 19.9 33-00 7.1 33.0. 174.8 25.6 7-24-78 Surface 30.0 32.30 5.2 13.0 83.2 0.8 Bottom 30.0 34.16 5.3 17.0 103.6 6.8 SB14 10-19-77 2 Surface 17.8 34.35 7.3 14.0 95.6 10.0 Bottom 17.5 34.35 7.4 19.0 127.6 24.8 2-1-78 Surface 5.3 30.89 10.6 9.7 - - Bottom 5.3 30.93 10.5 10.0 77.2 4.8 4-25-78 Surface 21.3 34.11 6.9 12.0 139.2 23.6 Bottom 21.0 32.92 7.0 12.0 128.4 21.6 7-24-78 Surface 29.4 34.29 6.0 17.0 122.8 29.2 Bottom 29.4 34.27 6.1 17.0 126.0 17.2 SB15 8-22-77 4 Surface 27.8 33.73 7.3 13.0 109.6 31.2 Bottom 27.0 33.57 5.6 30.0 178.4 34.8 2-1-78 Surface 4.9 30.87 10.4 11.0 95.2 18.0 Bottom 4.8 30.80 10.6 11.0 100.0 16.8 4-24-78 Surface 20.8 33.01 7.0 11.0 77.6 10.8 Bottom 19.9 33.00 6.9 33.0 188.4 49.2 7-24-78 Surface 29.7 34.33 5.8 12.0 114.8 8.6 Bottom 29.3 34.24 6.1 13.0 133.6 7.6 SB17 10-19-77 1 Surface 16.3 34.71 7.0 18.0 115.6 28.0 Bottom 16.3 34.72 7.2 17.0 135.6 12.0 2-1-78 Surface 4.9 30.70 10.3 29.0 - - Bottom 4.9 30.73 10.3 32.0 - - 4-25-78 Surface 21.8 32.79 6.5 16.0 125.2 10.0 Bottom 21.8 33.13 6.8 20.0 151.6 16.0 7-24-78 Surface 30.1 34.07 5.2 18.0 122.0 21.2 Bottom 30.1 34.03 5.0 42.0 176.8 24.8 SBI8 10-19-77 2 Surface 16.8 34.72 7.2 17.0 120.4 29.6 Bottom 16.7 34.73 7.1 21.0 152.0 22.4 2-1-78 Surface 4.9 30.59 10.6 17.0 78.0 12.4 Bottom 4.7 30.42 10.6 17.0 - - 4-24-78 Surface 19.6 33.10 6.8 - 135.6 20.4 Bottom 19.6 33.06 6.9 22.0 146.8 13.2 7-24-78 Surface 30.1 33.99 5.2 25.0 - - Bottom 30.0 33.97 5.0 51.0 181.2 30.4 *Samples contained too much silt to make an accurate analysis possible. Table 2. Occurrence of epifaunal invertebrates in dredge collections from station SBO1, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February May Late July Phylum Porifera Halichondria bowerbanki + Cliona sp. + Phylum Cnidaria Bougainvillia rugosa + Pandeidae (undet.) + + + Eudendrium carneum + Campanulina sp. + Clytia kincaidi + Obelia bidentata + + + Schizotricha tenella + Leptogorgia virgulata + + + Actiniaria (undet.) Phylum Entoprocta Barentsia laxa + Phylum Bryozoa Alcyonidium hauffi + Alcyonidium polyoum Anguinella palmata + + + + Amathia distans + Bowerbankia gracilis + Membranipora tenuis + + + + Electra monostachys + + + Bugula neritina + + Schizoporella errata + + + Hippoporina verrilli + + + Parasmittina nitida + + Cryptosula pallasi@na + + + Phylum Annelida Nereis succinea + + Sabellaria vulgaris + + + + Hydroides dianthus + Phylum Mollusca Acanthodoris pilosa + Brachidontes exustus + Ostrea equestris + + Phylum Artl@ropoda Balanus venustus + + Balanus improvisus + + Neopanope sayi + Panopeus herbstii + Phylum Echinodermata Sclerodactyla briareus + Ophiothrix angulata + + Phylum Chordata Didemnum. candidum + Molgula manhattensis + + No. Species 16 7 23 23 Sorensen Coefficient .43 .51 .51 12 Table 3. Occurrence of epifaunal invertebrates in dredge collections from station SB03, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February ApEil Late July Phylum Porifera Lissodendoryx carolinensis + + Microciona prolifera + + + Halichondria bowerbanki + + + + Cliona sp. + + + + Phylum Cnidaria Turritopsis nutricula + Bougainvillia rugosa + Pandeidae (undet.) + + Eudendrium carneum + + + Campanulina sp. + Clytia cyli@drica + Clytia kincaidi + Obelia bidentata + + Obelia dichotoma + Campano sis sp. + Dynamen cornicina + Sertularia stookeyi + + + Schizot@@icha tenella + + + Plumularia floridana + Leptogorgia virgulata + + + + Actiniaria (undet.) + + Phylum Platyhelminthes Stylochus ellipticus + Phylum Rhynchocoela Nemertean (undet.) + Phylum Entoprocta Loxosomella sp. + Pedicellina cernua + Barentsia laxa + + Phylum Bryozoa Alcyonidium hauffi + + 4- Anguinella palmata + + + + Amathia dis_t_.ns + + + Bowerbankia gracilis + + + Aeverrillia setigera + + + Membranipora arborescens + Membranipora tenuis + + + + Electra monostachys + + Synnotum aegyptiacum + + + Bugula neritina + + Schizop rella errata + + + Hippoporina verrilli + + + + Microporella ciliata + + + + Parasmittina nitida + + + + Phylum Annelida Nereis succinea + + + Sabellaria vulgaris + + + + Hydroides dianthus + + + + Phylum Mollusca Diodora cayenensis + Cerithiopsis greeni + + Crepidula fornicata + + Crepidula Plana + Mitrella lunata + Opisthobranchs (undet.) + Acanthodoris pilosa + + + + Chaetopleura apiculata + Ostrea equestris + + + + Crassostrea virginica + + Phylum Arthropoda Tanystylum orbiculare + + Callipallene brevirostrum + Balanus venustus + + + Balanus galeatus + + + Balanus improvisus + + + 13 Caprellidae (undet.) + + + + Palaemonetes vulgaris + Periclimenes longicaudatus + Alpheus normanni + + + Clibanarius vittatus + Pagurus longicarpus + Callinectes ornatus + Callinectes sapidus + Menippe mercenaria + + Neopanope sayi + + + + Eurypanopeus depressus + + Panopeus herbstii + + + Libinia sp. + Phylum Echinodermata Asterias forbesi + Hemipholis elongata + Ophiothrix angulata + + + Phylum Chordata Didemnum candidum + + Perophora viridis + + Molgula manhattensis + + + No. Species 45 32 47 46 Sorensen Coefficient .55 .61 .68 14 Table 4. Occurrence of epifaunal invertebrates in dredge collections from station SB04, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February April Late July Phylum Porifera Microciona prolifera + Halichondria bowerbanki + Cliona sp: + + Phylum Cnidaria Hydractiniidae (undet.) + Eudendrium carneum + + Clytia kincaidi + Dynamena cornicina + Sertularia stookeyi + Schizotricha tenella + + Plumularia floridana + Leptogorgia virgulata + + + Actiniaria (undet.) + Phylum Platyhelminthes Stylochus ellipticus Phylum Entoprocta Loxosomella sp. + Barentsia laxa + + Phylum Bryozoa Nolella stipata + Anguinella palmata + + Amathia distans + Bowerbankia gracilis + + Aeverrillia setigera + Membranipora tenuis + Synnotum aegyptiacum + + Bugula neritina + + Schizoporella errata + + Hippoporina verrilli + + Microporella ciliata + + Parasmittina nitida + + Phylum Annelida Nereis succinea + Sabellidae (undet.) + Hydroides dianthus + Oligochaeta (undet.) + Phylum Mollusca Crepidula fornicata + + Simnia uniplicata + Anachis avara + Busycon canaliculatum + Ilyanassa obsoleta + Acanthodoris pilosa + + Ostrea equestris + + Crassostrea virginica + Phylum Arthropoda Balanus venustus + Balanus galeatus + + Caprellidae (undet.) + + Alpheus normanni + + Callinectes sapidus + + Eurypanopeus depressus + Panopeus herbstii + Neopanope sayi + Libinia sp. + Phylum Echinodermata Sclerodactyla briareus + + Hemipholis elongata + + Ophiothrix angulata + Phylum Chordata Didemnum candidum + + Perophora viridis + MoIgula manhattensis + + Ascidiacea (undet.) + No. Species 40 6 5 29 Sorensen Coefficient .04 .09 .55 15 Table 5. Occurrence of epifaunal invertebrates in dredge collections from station SB05, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species Aucnist Late July Phylum Porifera Halichondria bowerbanki + Cliona sp. + + Phylum Cnidaria Ectopleura dumortieri + Pandeidae (undet.) + Eudendrium carneum + Clytia kincaidi + Obelia bidentata + + Sertularia stookeyi + Schizotricha tenella + + Leptogorgia virguITta + + Actiniaria (undet.) + + Phylum Entoprocta Loxosomella sp. + Phylum Bryozoa Alcyonidium hauffi + + Alcyonidium polyoum + Anguinella palmata + + + + Amathia distans + + Bowerbankia gracilis + + + Aeverrillia setigera + + Membranipora arborescens + Membranipora tenuis + + + Electra monostachys + Bugula neritina + + Schizoporella errata + + + Hippoporina verrilli + + Microporella ciliata + Parasmittina nitida + + + Cryptosula pallasiana + + Phylum Annelida Lepidonotus sublevis + Sabellaria vulgaris + + + Hydroides dianthus + + Phylum Mollusca Crepidula fornicata + Crepidula plana + Phylum Arthropoda Balanus venustus + Penaeus aztecus + Pagurus longicarpus + Neopanope sayi + + Eurypanopeus depressus + Phylum Echinodermata Sclerodactyla briareus + Ophiothrix angulata + + + Phylum Chordata Perophora viridis + Molgula manhattensis + Ascidiacea (undet.) + No. Species 31 3 20 16 Sorensen Coefficient .12 .47 .47 16 Table 6. Occurrence of epifaunal invertebrates in dredge collections from station SB07, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February May September Phylum Porifera Lissodendoryx carolinensis + + + Microciona prolifera + + Halichondria bowerbanki + Cliona sp. + + + Porifera (undet.) + Phylum Cnidaria Pandeidae (undet.) + + Eudendrium carneum + + + Cuspidella humilis + Lovenella grandis + + Clytia kincaidi + + + Clytia paulensis + + Obelia bidentata + + Campanopsis sp. + Dynamena cornicina + Sertularia stookeyi + Schizotricha tenella + + Leptogorgia virgulata + + + + Actiniaria (undet.) + + + + Phylum Entoprocta Loxosomella sp. + Barentsia laxa + + + Phylum Bryozoa Alcyonidium hauffi + + Anguinella palmata + + + + Amathia distans + + + Bowerbankia gracilis + + + Aeverrillia setigera + + + Membranipora arborescens + Membranipora tenuis + + + Electra monostachys + + Synnotum aegyptiacum + + Bugula neritina + + + Schizoporella errata + + + + Hippoporina verrilli + + + + Microporella ciliata + + + Parasmittina nitida + + + + Phylum Annelida Nereis succinea + + Sabellidae (undet.) + Sabellaria vulgaris + + + + Hydroides dianthus + + + + Phylum Mollusca Crepidula fornicata + Eupleura caudata + Cerithiopsis greeni + Ilyanassa obsoleta + Acanthodoris pilosa + + Chaetopleura apiculata + Brachidontes exustus + Ostrea equestris + + + Crassostrea virginica + + Phylum Arthropoda Callipallene brevirostrum + Balanus galeatus + Balanus improvisus + + + Anthuridae (undet.) + Caprellidae (undet.) + + Penaeus duorarum + Alpheus armillatus + Alpheus normanni + + Pagurus longicarpus + Callinectes sapidus + Hexapanopeus angustifrons + 17 Table 6. (cont.) Species August February May September Neopanope sayi + + + Eurypanopeus depressus + Panopeus herbstii + + Libinia sp. + + Phylum Echinodermata Ophiothrix angulata + + + + Phylum Chordata Didemnum candidum + + Perophora viridis + + + Molgula manhattensis + + + + No. Species 30 31 48 34 Sorensen Coefficient .49 .54 .59 18 Table 7. Occurrence of epifaunal invertebrates in dredge collections from station SB08, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February May Late July Phylum Porifera Lissodendoryx carolinensis + + Microciona prolifera + + + + Halichondria bowerbanki + + + Cliona sp. + + + + Phylum Cnidaria Turritopsis nutricula + Bougainvillia rugosa + Pandeidae (undet.) + "Perigonimus' sp. + Eudendrium carneum + + + Lovenella grandis + Clytia kincaidi + + + Obelia bidentata + + Schizotricha tenella + + + Plumularia floridana + Leptogorgia virgulata + + + Actiniaria (undet.) + Phylum Entoprocta Loxosomella sp. + Pedicellina cernua + Barentsia laxa + + + Barentsia sp. + Phylum Bryozoa Crisia sp. + Anguinella palmata + + + Bowerbankia gracilis + + + + Aeverrillia setigera + + Membranipora arborescens + Membranipora tenuis + + + + Conopeum tenuissimum + Electra monostachys + Synnotum aegyptiacum + Bugula neritina + + + Schizoporella errata + + + + Hippoporina verrilli + + + + Microporella ciliata + + + + Parasmittina nitida + + + + Phylum Annelida Nereis succinea + + Lepidonotus sublevis + Sabellaria @@@ + + + Hydroides dianthus + + + Polydora sp. + Phylum Mollusca Crepidula fornicata + + + Crepidula Plana + Simnia uniplicata + Urosalpinx cinerea + Acanthodoris pilosa + Ostrea equestris + + + Crassostrea virginica + + + + Phylum Arthropoda Tanystylum orbiculare + Balanus venustus + + Balanus improvisus + + + Caprellidae (undet.) + + Penaeus aztecus + Penaeus uorarum + Portunus gibbesii + Callinectes ornatus + Callinectes sapidus + Menippe mercenaria + + Hexapanopeus angustifrons + Neopanope sayi + Eurypanopeus depressus + + + Panopeus herbstii + + + 19 Table 7. (cont.) Species August February May Late July Phylum Echinodermata Sclerodactyla briareus + Ophiothrix angulata + + + Phylum Chordata Perophora viridis + + + Molgula manhattensis + + + No. Species 35 24 40 36 Sorensen Coefficient .51 .67 .65 20 Table 8. Occurrence of epifaunal invertebrates in dredge collections from station SB10, Sewee Bay, Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August Feburary April Late July Phylum Porifera Microciona prolifera + Halichondria bowerbanki + + Cliona sp. + Phylum Cnidaria Turritopsis nutricula + Pandeidae (undet.) + Eudendrium carneum + Clytia kincaidi + + Obelia bidentata + Dynamena cornicina + + Sertularia stookeyi + Schizotricha tenella + Leptogorgia virgulata + + Actiniaria (undet.) + Phylum Entoprocta Barentsia laxa + + Phylum Bryozoa Anguinella palmata + + Amathia distans + Bowerbankia gracilis + + + Aeverrillia setigera + + Membranipora arborescens + Membranipora tenuis + + + Electra monostachys + Bugula neritina + + Schizoporella errata + + Hippoporina verrilli + + Microporella ciliata + + Parasmittina nitida + Cryptosula pallasiana + Phylum Annelida Sabellaria vulgaris + + Hydroides dianthus + + Phylum Mollusca Simnia uniplicata + Ilyanassa obsoleta + Ostrea equestris + Phylum Arthropoda Balanus venustus + + Balanus improvisus + Pagurus longicarpus + Eurypanopeus depressus + + + Phylum Echinodermata Hemipholis elongata + Ophiothrix angulata + Phylum Chordata Perophora viridis + Molgula manhattensis + + No. Species 28 3 4 26 Sorensen Coefficient .06 13 .67 21 Table 9. Occurrence of epifaunal invertebrates in dredge collections from station SB12, Sewee Bay. Collections were taken before, immediately after and three months after dredging, as well as one year after the pre-dredge survey. Species August February May September Phylum Mollusca Nassarius vibex + Ilyanassa obsoleta + + Phylum Arthropoda Penaeus aztecus + Callinectes sapidus + + Phylum Chordata Molgula manhattensis + No. Species 3 2 1 1 Sorensen Coefficient 0.40 0.00 0.00 22 Table 10. Occurrence of epifaunal invertebrates in dredge collections from station SB13, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February April Late July Phylum Porifera Lissodendoryx carolinensis + Microciona prolifera + Cliona sp. + + + + Phylum Cnid aria Ectopleura dumortieri + Hydractiniidae (undet.) + + Pandeidae (undet.) + + + + Amphinema dinema + Eudendrium carneum + + + Campanulina sp. + Lovenella grandis + Clytia kincaidi + + + Clytia paulensis + Obelia bidentata + Obelia dichotoma + Dynamena cornicina + Schizotricha tenella + + + Leptogorgia virgulata + + + Actiniaria (undet.) + + Phylum Entoprocta Pedicellina cernua + + Barentsia laxa + + + Phylum Bryozoa Alcyonidium hauffi + Anguinella palmata + + + + Bowerbankia gracilis + + + + AeverrTllia setigera + + Membranipora arborescens + Membranipora tenuis + + + + Electra monostachys + Synnotum aegyptiacum + Schizoporella errata + + + + Hippoporina verrilli + + + + Microporella ciliata + + + + Parasmittina nitida + + Phylum Annelida Nereis succinea + + Lepidonotus sublevis + Sabellaria vulgaris Hydroides dianthus + + + Sabellidae (undet.) + + Phylum Mollusca Littorina irrorata + Crepidula fornicata + Crepidula plana + Simnia uniplicata + Urosalpinx cinerea + Ilyanassa obsoleta + + Acanthodoris pilosa + + Ostrea equestris + + + Crassostrea virginica + Phylum Arthropoda Callipallene brevirostrum + Balanus galeatus + Balanus improvisus + + Cyathura burbancki + Penaeus aztecus + Clibanarius vittat-us. + Callinectes sapidus + Menippe mercenaria + Hexapanopeus angustifrons + Panopeus herbstii + Phylum Echinodermata Sclerodactyla briareus + Ophiothrix angulata + + 23 Table 10. (cont.) Species August February April Late July Phylum Chordata Didemnum candidum + Perophora viridis + Molgula manhattensis + + + + No. Species 31 22 25 37 Sorensen Coefficient .45 .57 .62 24 Table 11. Occurrence of epifaunal invertebrates in dredge collections from station SB14, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February April Late July Phylum Porifera Microciona prolifera + + + + Cliona sp. + + + + Phylum Cnidaria Ectopleura dumortieri + Bougainvillia rugosa + Pandeidae (undet.) + tudendrium carneum + + Campanulina sp. + + + Lovenella gracilis + + Lovenella grandis + + + Clytia kincaidi + + Obelia bidentata + + Obelia dichotoma + @@@ SP. + Schizotricha tenella + + Leptogorgia virgulata + + + + Actinia:ria (undet.) + + + Phylum Platyhelminthes Stylochus ellipticus + + Phylum Rhynchocoela Nemertean (undet.) + Phylum Entoprocta Barentsia laxa + + + + Phylum Bryozoa Alcyonidium hauffi + Alcyonidium mammillatum + Anguinella palmata + + + + Arnathia distans + + Bowerbankia gracilis + + + + Aeverrillia setigera + + + + Membranipora arborescens + Membranipora tenuis + + + + Electra monostachys + + Bugula neritina + + + Schizoporella errata + + + + Hippoporina verrilli + + + + Parasmittina nitida + + + + Cryptosula pallasiana + + Phylum Annelida Nereis succinea + Sabellaria vulgaris + + + + Hydroides dianthus + + + + Polydora sp. + Phylum Mollusca Crepidula fornicata + + Simnia uniplicata + Acanthodoris pilosa + + + Brachidontes exustus + + Ostrea equestris + + + + Crassostrea virginica + + Phylum Arthropoda Tanystylum orbiculare + Balanus venustus + + Balanus galeatus + Balanus improvisus + + + + Caprellidae (undet.) + + Penaeus aztecus + + Palaemonetes vulgaris + Clibanarius vittatus + Callinectes sapidus + + 25 Table 11. (cont.) Species August February April Late July Neopanope sayi + Eurypanopeus depressus + + Panopeus herbstii + + Phylum Echinodermata Ophiothrix angulata + Phylum Chordata Didemnum candidum + + + Perophora viridis + + Molgula manhattensis + + + + No. Species 31 36 38 34 Sorensen Coefficient .63 .55 .65 26 Table 12. Occurrence of epifaunal invertebrates in dredge collections from station SB15, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February May Late July Phylum Porifera Microciona prolifera + Halichondria bowerbanki + + + Cliona sp. + + + Phylum Cnidaria Turritopsis nutricula + Pandeidae (undet.) + Eudendrium album + Campanulina sp. + + Clytia kincaidi + + Obelia bidentata + + Dynamena cornicina + Sertularia stookeyi + + Schizotricha tenella + + + Leptogorgia virgulata + + + Astrangia danae + Actiniaria (undet.) + + + Phylum Entoprocta Barentsia laxa + + + Phylum Bryozoa Alcyonidium hauffi + + + Alcyonidium polyoum + Anguinella palmata + + + + Bowerbankia gracilis + + Aeverrillia setigera + + + Membranipora arborescens + Membranipora tenuis + + + + Electra monostachys + + Bugula neritina + + + Schizoporella errata + + + Hippoporina verrilli + + Microporella ciliata + + Parasmittina nitida + + + Cryptosula pallasiana + Phylum Annelida Nereis succinea + Lepidonotus sublevis + Sabellaria vulgaris + + Hydroides dianthus + Phylum Mollusca Simnia uniplicata + Anadara transversa + Brachidontes exustus + Pteria colymbus + Ostrea equestris + + Phylum Arthropoda Balanus venustus + Balanus galeatus + Balanus improvisus + + + + Penaeus aztecus + Penaeus duorarum + Alpheus normanni + Pagurus longicarpus + Neopanope sayi + Eurypanopeus depressus + + Squilla empusa + Phylum Echinodermata Hemipholis elongata + Ophiothrix angulata + + + Phylum Chordata Didemnum candidum + Perophora viridis + Molgula manhattensis + + + Ascidiacea (undet.) + + No. Species 36 11 31 24 Sorensen Coefficient .30 .60 .53 27 Table 13. Occurrence of epifaunal invertebrates in dredge collections from station SB17, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February May September Phylum Porifera Microciona prolifera + Phylum Cnidaria Pandeidae (undet.) + Eudendrium carneum + + Lovenella grandis + Clytia kincaidi + Schizotricha tenella + + Leptogorgia virgulata + + Phylum Bryozoa Victorellidae (undet.) + Anguinella palmata + + + Amathia distans + + Bowerbankia gracilis + + + Aeverrillia setia@@ + Membranipora tenuis + Parasmittina nitida + Phylum Molluscs Ilyanassa obsoleta + + Phylum Arthropoda Callinectes sapidus + + Panopeus herbstii + Phylum Echinodermata Ophiothrix angulata + Phylum Chordata Perophora viridis + MoIgula manhattensis + + No. Species 12 5 6 8 Sorensen Coefficient 0.35 0.11 0.50 28 Table 14. Occurrence of epifaunal invertebrates in dredge collections from station SB18, Sewee Bay. Collections were taken before, immediately after, and three months after dredging, as well as one year after the pre-dredge survey. Species August February April Late July Phylum Porifera Lissodendoryx carolinensis + + Microciona prolifera + + Halichondria bowerbanki + + + Cliona sp. + + + + Porifera (undet.) + + Phylum Cnidaria Ectopleura dumortieri + Turritopsis nut.ricula + Pandeid-ae- (i et.) + + Eudendrium carneum + + Campanulina sp. + + Lovenella gracilis + Lovenella grandis + + Clytia cylindrica + Clytia kincaidi + + + Obelia bidentata + Schizotricha tenella + + + Plumularia floridana + Leptogorgia virgulata Actiniaria (undet.) + + + + Phylum Entoprocta Pedicellina cernua + + Barentsia laxa + + + Phylum Bryozoa Alcyonidium hauffi + Anguinella palmata + + + + Amathia distans + + + + Bowerbankia gracilis + + + + Aeverrillia setigera + Membranipora arborescens + Membranipora tenuis + + + + Electra monostachys + + Synnotum aegyptiacum + + + Bugula neritina + Schizoporella errata + + + + Hippoporina verrilli + + + + Microporella ciliata + + + + Parasmittina nitida + + + + Phylum Annelida Nereis succinea + Lepidonotus sublevis + + Sabellaria vulgaris + + + Hydroides dianthus + + + + Phylum Mollusca Crepidula fornicata + + Simnia uniplicata + Eupleura caudata + Fasciolaria lilium hunteria + + Nassarius vibex + Acanthodoris pilosa + + + Anadara transversa + Ostrea equestris + + Phylum Arthropoda Tanystylum orbiculare + + Balanus galeatus + + Balanus improvisus + + + Caprellidae (undet.) + + Penaeus duorarum + Trachypenaeus constrictus + Alpheus heterochaelis + Alpheus normanni + Portunus gibbesii + Callinectes sapidus + + Neopanope sayi + Eurypanopeus depressus + Panopeus herbstii + 29 Table 14. (cont.) Species August February April Late July Phylum Echinodermata Ophiothrix angulata + + + Phylum Chordata Didemnum.candidum + Perophora viridis + Molgula manhattensis + + + + Ascidiacea (undet.) + No. Species- 37 32 36 34 Sorensen Coefficient .52 .66 .62 30 Table 15. Macroinvertebrate species collected from the Sewee Bay channel station, SBOl. (A = Amphipoda; C = Cumacea; D - Decapoda; H = Hemichordata; I = Isopoda; M = Mollusca; My = Mysidacea; 0 = Ophiuroidea; P = Polychaeta). SBOl Rank Total Number/0.05 m2 Estimated by Species Number Y SD Number/m2 Number ----------------------------------- Collection Date 23 August 1977 ------------------------------------ Paraprionospio pi-anata (P) 38 12.7 2.3 230 1.0 Ogyrides limicola (D) 10 3.3 1.2 61 2.0 Lumbrineris tenuis (P) 6 2.0 1.0 36 3.0 Notomastus lobatus (P) 4 1.3 1.5 24 4.0 Glycinde solitaria (P) 3 1.0 1.0 18 5.0 Aricidea fragilis M 2 0.7 0.6 12 6.0 Saccoglossus kowalevskii (H) 1 0.3 0.6 6 8.0 Glycera americana (P) 1 0.3 0.6 6 8.0 Haploscoloplos fragilis (P) 1 0.3 0.6 6 8.0 ----------------------------------- Collection Date 16 January 1978 ----------------------------------- Paraprionospio pinnata (P) 14 4.7 2.5 85 1.0 Ogyrides limicola (D) 11 3.7 2.3 67 2.0 Gattyana cirrosa (P) 2 0.7 1.2 12 3.5 Aricidea fragilis M 2 0.7 1.2 12 3.5 Mysidopsis bigelowi (My) 1 0.3 0.6 6 6.0 Amphiodia planispina (0) 1 0.3 0.6 6 6.0 Glycera americana (P) 1 0.3 0.6 6 6.0 ----------------------------------- Collection Date 28 April 1978 ------------------------------------ Melita appendiculata.(A) 26 8.7 15.0 158 1.0 Paraprionospio pinnata (P) 15 5.0 6.0 91 2.0 Nereis succinea (P) 4 1.3 2.3 24 3.0 Eurypanopeus depressus (D) 2 0.7 1.2 12 7.5 Paracaprella tenuis (A) 2 0.7 1.2 12 7.5 Ophiothrix angulata (0) 2 0.7 1.2 12 7.5 Mulinia lateralis (M) 2 0.7 1.2 12 7.5 Scoloplos sp. (P) 2 0.7 0.6 12 7.5 Lumbrineris tenuis M 2 0.7 1.2 12 7.5 Haploscoloplos fragilis (P) 2 0.7 1.2 12 7.5 Sabella microphthalma (P) 2 0.7 1.2 12 7.5 Ogyrides limicola (D) 1 0.3 0.6 6 19.5 Neopanope texana (D) 1 0.3 0.6 6 19.5 Ampelisca vadorum (A) 1 0.3 0.6 6 19.5 Lembos websteri (A) 1 0.3 0.6 6 19.5 Leucon americanus (C) 1 0.3 0.6 6 19.5 Cyathura burbanki (1) 1 0.3 0.6 6 19.5 Actiniaria (undet.) 1 0.3 0.6 6 19.5 Glycera americans (P) 1 0.3 0.6 6 19.5 Heteromastus filiformis (P) 1 0.3 0.6 6 19.5 Glycinde solitaria (P) 1 0.3 0.6 6 19.5 Marphysa sanguinea (P) 1 0.3 0.6 6 19.5 Diopatra cuprea (F) 1 0.3 0.6 6 19.5 Arabella iricolor (P) 1 0.3 0.6 6 19.5 Drilonereis magna (P) 1 0.3 0.6 6 19.5 Aricidea fragilis (P) 1 0.3 0.6 6 19.5 Cirratulidae (undet.) M 1 0.3 0.6 6 19.5 ------------------------------------ Collection Date 3 August 1978 ----------------------------------- Ogyrides limicola (D) 21 7.0 4.4 127 1.0 Heteromastus filiformis M 2 0.7 0.6 12 3.0 Lumbrineris t-en-uis(P) 2 0.7 0.6 12 3.0 Haploscoloplos fragilis (P) 2 0.7 1.2 12 3.0 Mytilidae(undet.)(M) 1 0.3 0.6 6 6.0 Nereis succinea (P) 1 0.3 0.6 6 6.0 Paraprionospio pinnata M 1 0.3 0.6 6 6.0 31 Table 16. Macroinvertebrate species collected from the Sewee Bay intertidal station, SB02. (A Amphipoda; D = Decapoda; I = Isopoda; M = Molluscs; P = Polychaeta). SB02 2 Rank Total Number/0.05m Estimated by Species Number 7 SD Number/m2 Number ----------------------------------- Collection Date 30 August 1977 ---------------------------------- Lumbrineris tenuis (P) 17 5.7 3.5 103 1.0 Aricidea fragilis (P) 15 5.0 2.0 91 2.0 Glycera americana (P) 3 1.0 1.0 18 3.0 Alpheus normanni (D) 2 0.7 1.2 12 4.0 Scoloplos sp. (P) 1 0.3 0.6 6 6.0 Glycinde solitaria (P) 1 0.3 0.6 6 6.0 Haploscoloplos fragilis (P) 1 0.3 0.6 6 6.0 ----------------------------------- Collection Date 16 January 1978-7 ------------------------------- Heteromastus filiformis (P) 8 2.7 2.1 48 1.0 Lumbrineris tenuis (P) 7 2.3 2.1 42 2.0 Mercenaria mercenaria (M) 5 1.7 0.6 30 3.0 Glycera americans (P) 4 1.3 0.6 24 4.0 Tellinidae (undet.) (M) 2 0.7 0.6 12 5.0 Nemertina (undet.) 1 0.3 0.6 6 7.5 Turbonilla sp. (M) 1 0.3 0.6 6 7.5 Paraprionospio pinnata (P) 1 0.3 0.6 6 7.5 Maldanidae (undet.) (P) 1 0.3 0.6 6 7.5 ------------------------------------ Collection Date = 25 April 1978 --------------------------------- Nereis succinea (P) 88 29.3 19.3 533 1.0 Uca sp. (D) 1 0.3 0.6 6 2.5 Cyathura burbanki (1) 1 0.3 0.6 6 2.5 ------------------------------------ Collection Date = 3 August 1978 --------------------------------- Scoloplos rubra (P) 3 1.0 1.0 18 1.5 Heteromastus filiformis (P) 3 1.0 1.7 18 1.5 Alpheus heterochaelis '(D) 2 0.7 1.2 12 4.0 Lumbrineris tenuis (P) 2 0.7 1.2 12 4.0 Haploscoloplos fragilis (P) 2 0.7 1.2 12 4.0 Gammarus palustris (A) 1 0.3 0.6 6 7.5 Glycera americana (P) 1 0.3 0.6 6 7.5 Scoloplos sp. (P) 1 0.3 0.6 6 7.5 Drilonereis magna (P) 1 0.3 0.6 6 7.5 32 Table 17. Macroinvertebrate species collected from the Sewee Bay channel station, SB03. (A Amphipoda; C = Cumacea; D = Decapoda; I = Isopoda; M = Mollusca; P = Polychaeta). SB03 Rank Total Number/0.05m 2 Estimated by Species Number -9 SD Number/m2 Number ------------------------------------ Collection Date = 30 August 1977 ------------------------------------ Lumbrineris tenuis (P) 26 8.7 3.1 158 1.0 Diptera (undet.) 1 0.3 0.6 6 2.5 Glycera americana (P) 1 0.3 0.6 6 2.5 ------------------------------------ Collection Date 16 January 1978 ----------------------------------- Heteromastus filiformis (P) 4 1.3 0.6 24 1.5 Lumbrineris tenuis (P) 4 1.3 1.2 24 1.5 Caprella equilibra (A) 3 1.0 1.7 18 3.5 Paraprionospio pinnata (P) 3 1.0 0.0 18 3.5 Melita dentata (A) 2 0.7 1.2 12 5.5 Nereis succinea (P) 2 0.7 0.6 12 5.5 Alpheus heterochaelis '(D) 1 0.3 0.6 6 11.0 Pinnixa sayana (D) 1 0.3 0.6 6 11.0 Cyathura burbanki (1) 1 0.3 0.6 6 11.0 Mitrella lunata (M) 1 0.3 0.6 6 11.0 Glycera americana (P) 1 0.3 0.6 6 11.0 Glycinde solitaria (P) 1 0.3 0.6 6 11.0 Arabella iricolor (P) 1 0.3 0.6 6 11.0 Aricidea fragilis (P) 1 0.3 0.6 6 11.0 Cirratulidae (undet.) (P) 1 0.3 0.6 6 11.0 ------------------------------------- Collection Date = 24 April 1978 ------------------------------------ Ampelisca vadorum (A) 18 6.0 1.0 109 1.0 Lumbrineris tenuis (P) 16 5.3 2.3 97 2.0 Streblospio benedicti (P) 5 1.7 2.9 30 3.0 Mulinia lateralis (A) 4 1.3 0.6 24 5.0 Tellinidae (undet.)(M) 4 1.3 1.5 24 5.0 Mediomastus californiensis (P) 4 1.3 2.3 24 5.0 Erichthonius brasiliensis (A) 3 1.0 1.7 18 8.5 Glycera americana (P) 3 1.0 1.7 18 8.5 Tharyx marioni (P) 3 1.0 1.0 18 8.5 Haplosco,loplos sp. (P) 3 1.0 1.0 18 8.5 Ogyrides limicola (D) 2 0.7 0.6 12 13.5 Oxyurostylis smithi (C) 2 0.7 0.6 12 13.5 Nemertina (undet.) 2 0.7 0.6 12 13.5 Pelecypoda (undet.) (M) 2 0.7 0.6 12 13.5 Glycinde solitaria (P) 2 0.7 0.6 12 13.5 Paraprionospio pinnata (P) 2 0.7 0.6 12 13.5 Portunidae (undet.) (D) 1 0.3 0.6 6 20.0 Caprellidae (undet.) (A) 1 0.3 0.6 6 20.0 Acteocina canaliculata (M) 1 0.3 0.6 6 20.0 Heteromastus filiformis (P) 1 0.3 0.6 6 20.0 Nereis succinea (P) 1 0.3 0.6 6 20.0 Aricidea fragilis (P) 1 0.3 0.6 6 20.0 Maldanidae (undet.) (P) 1 0.3 0.6 6 20.0 ------------------------------------ Collection Date 17 August 1978 ------------------------------------ Ogyrides limicola (D) 5 1.7 0.6 30 1.0 Paraprionospio pinnata (P) 3 1.0 1.7 18 2.0 Callianassa atla-ntica (D) 2 0.7 1.2 12 5.0 Glycera americana (P) 2 0.7 0.6 12 5.0 Glycinde solitaria (P) 2 0.7 0.6 12 5.0 Aricidea fragilis (P) 2 0.7 1.2 12 5.0 Clymenella torquata (P) 2 0.7 0.6 12 5.0 Stomatopoda (undet.) 1 0.3 0.6 6 10.5 Pelecypoda (undet.) (M) 1 0.3 0.6 6 10.5 Scoloplos sp. (P) 1 0.3 0.6 6 10.5 Lumbrineris tenuis (P) 1 0.3 0.6 6 10.5 Notomastus sp. (P) 1 0.3 0.6 6 10.5 Asychis carolinae (P) 1 0.3 0.6 6 10.5 33 Table 18. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB04. (A = Amphipoda; D = Decapoda; H Hemichordata; M = Molluscs; 0 = Ophiuroidea; S = Stomatopoda; P = Polychaeta). SB04 2 Rank Total Number/0.05m Estimated by Species Number -9 SD Number/m2 Number ----------------------------------- Collection Date 30 August 1977 ----------------------------------- Scoloplos rubra (P) 7 2.3 1.5 42 1.0 Ogyrides limicola (D) 4 1.3 1.5 24 3.0 Lumbrineris tenuis (P) 4 1.3 1.2 24 3.0 Glycinde solitaria (P) 4 1.3 0.6 24 3.0 Glycera americana (P) 3 1.0 0.0 18 5.5 Aricidea fragilis (P) 3 1.0 1.7 18 5.5 Squilla empusa (S) 1 0.3 0.6 6 9.5 Hemipholis elongata (0) 1 0.3 0.6 6 9.5 Anadara ovalis (M) 1 0.3 0.6 6 9.5 Diplodonta sp. (M) 1 0.3 0.6 6 9.5 Nereis succinea (P) 1 0.3 0.6 6 9.5 -5rilone@reismagna (P) 1 0.3 0.6 6 9.5 ----------------------------------- Collection Date 16 January 1978 --------------------------------- Paraprionospio pinnata (P) 17 5.7 2.1 103 1.0 Heteromastus filiformis (P) 5 1.7 0.6 30 2.0 Ogyrides limfc-ola (D) 3 1.0 0.0 18 3.0 Lumbrineris tenuis (P) 2 0.7 0.6 12 4.0 Batea cathar-inensis (A) 1 0.3 0.6 6 9.0 Zaprella equilibra (A) 1 0.3 0.6 6 9.0 §accoglossus k@-w-alevskii (H) 1 0.3 0.6 6 9.0 -Rulinia lateralis (M) 1 0.3 0.6 6 9.0 Scoloplos rubra (P) 1 0.3 0.6 6 9.0 Arabella iricolor (P) 1 0.3 0.6 6 9.0 Drilonereis magna (P) 1 0.3 0.6 6 9.0 Eteone heteropoda (P) 1 0.3 0.6 6 9.0 Haploscoloplos robustos (P) 1 0.3 0.6 6 9.0 ------------------------------------ Collection Date 24 April 1978 ---------------------------------- Ampelisca vadorum (A) 12 4.0 1.7 73 1.0 Lumbrineris tenuis (P) 10 3.3 3.5 61 2.0 Paraprionospio-pinnata (P) 9 3.0 1.0 55 3.0 Ogyrides limicola (D) 2 0.7 0.6 12 5.0 Tellinidae (undet.) (M) 2 0.7 0.6 12 5.0 Drilonereis magna (P) 2 0.7 0.6 12 5.0 Pelecypoda (undet. ) (M) 1 0.3 0.6 6 10.5 Mulinia lateralis (M) 1 0.3 0.6 6 10.5 Acteocina canaliculata (M) 1 0.3 0.6 6 10.5 Glycera americana (P) 1 0.3 0.6 6 10.5 Heteromastus filiformis (P) 1 0.3 0.6 6 10.5 Glycinde solitaria (P) 1 0.3 0.6 6 10.5 Aricidea fragilis (P) 1 0.3 0.6 6 10.5 Haploscoloplos.sp. (P) 1 0.3 0.6 6 10.5 ----------------------------------- Collection Date 17 August 1978 ---------------------------------- Ogyrides limicola (D) 36 12.0 3.0 218 1.0 Paraprionospio.pinnata (P) 10 3.3 3.2 61 2.0 Haploscoloplos fragilis (P) 6 2.0 1.7 36 3.0 Lumbrineris tenuis (P) 3 1.0 1.0 18 4.0 @iricidea fragilis (P) 2 0.7 0.6 12 5.0 Tellinidae (undet.) (M) 1 0.3 0.6 6 7.5 Glycera americans (P) 1 0.3 0.6 6 7.5 Glycinde solitaria (P) 1 0.3 0.6 6 7.5 Diopatra cuprea (P) 1 0.3 0.6 6 7.5 34 Table 19. Macroinvertebrate species collected from the Sewee Bay channel station, SB05. (A Amphipoda; C = Cumacea; D = Decapoda; I - Isopoda; M = Mollusca; 0 = Ophiuroidea; P = Polychaeta). SB05 Rank Total Number/0.05m2 Estimated by Species Number 'i SD Number/m2 Number ----------------------------------- Collection Date 23 August 1977 -------------------------------------- Paraprionospio pinnata (P) 27 9.0 2.7 164 1.0 lumbrineris ten@u-is(P) 5 1.7 0.6 30 2.0 Glycera americana (P) 3 .1.0 1.0 18 3.0 Hemipholis elo a (0) 2 0.7 0.6 12 4.5 Scoloplos rubra (P) 2 0.7 0.6 12 4.5 Ogyrides limicola (D) 1 0.3 0.6 6 8.5 Polinices dglicatus (M) 1 0.3 0.6 6 8.5 Mulinia lateralis (M) 1 0.3 0.6 6 8.5 Ilyanassa obsoleta (M) 1 0.3 0.6 6 8.5 -dlycinde s-olitaria (P) 1 0.3 0.6 6 8.5 Aricidea fragilis (P) 1 0.3 0.6 6 8.5 ----------------------------------- Collection Date 30 January 1978 ------------------------------------- Mulinia lateralis (M) 7 2.3 1.5 42 1.0 6gyrides limicola (D) 3 1.0 1.0 12 2.0 Leucon americanus; (C) 2 0.6 0.6 12 3.5 Nereis succinea (P) 2 0.6 1.2 12 3.5 Palaemonetes vulgaris (D) 1 0.3 0.6 6 9.0 Callinectes ornatus (D) 1 0.3 0.6 6 9.0 Caprella equilibra (A) 1 0.3 0.6 6 9.0 Mercenaria mercenaria (M) 1 0.3 0.6 6 9.0 Abra aegualis (M) 1 0.3 0.6 6 9.0 Pectinaria gouldii (P) 1 0.3 0.6 6 9.0 _ffeteromastus filiformis (P) 1 0.3 0.6 6 9.0 Arabella iricolor (P) 1 0.3 0.6 6 9.0 Paraprionospio pinnata (P) 1 0.3 0.6 6 9.0 ------------------------------------ Collection Date 28 April 1978 -------------------------------------- Haploscoloplos sp. (P) 10 3.3 4.9 61 1.0 Mulinia lateralis (M) 8 2.7 2.9 48 2.0 Ogyrides limicola (D) 4 1.3 1.2 24 3.0 Heteromastus filiformis (P) 3 1.0 1.0 18 4.5 Paraprionospio pinnata (P) 3 1.0 1.7 18 4.5 Teucon americanus (C) 2 0.7 0.6 12 6.5 Glycera americana (P) 2 0.7 0.6 12 6.5 Ampelisca vadorum (A) 1 0.3 0.6 6 9.5 Edotea montosa (f) 1 0.3 0.6 6 9.5 Tolinices duplicatus (M) 1 0.3 0.6 6 9.5 Tharyx marioni (P) 1 0.3 0.6 6 9.5 ------------------------------------ Collection Date 3 August 1978 ------------------------------------- Ogyrides limicola (D) 3 1.0 1.7 18 1.0 Zlycera am-ericana (P) 2 0.7 0.6 12 3.0 Heteromastus filiformis (P) 2 0.7 0.6 12 3.0 -@araprionospio pinnata (P) 2 0.7 1.2 12 3.0 Lumbrineris tenuis (P) 1 0.3 0.6 6 5.5 -Brilonereis magna (P) 1 0.3 0.6 6 5.5 35 Table 20. Macroinvertebrate species collected from the Sewee Bay intertidal station, SB06. (I Isopoda; M = Mollusca; P = Polychaeta). SB06 Rank Total Number/0.05m2 Estimated by Species Number 'K SD Number/m2 Number ------------------------------------ Collection Date 30 August 1977 ------------------------------------ Lumbrineris tenuis (P) 12 4.0 1.0 73 1.0 'Nereis succinea (P) 7 2.3 1.2 42 2.0 Aricidea fragilis (P) 4 1.3 0.6 24 3.0 Drilonereis magna (P) 2 0.7 0.6 12 4.0 Cyathura burbanki (1) 1 0.3 0.6 6 6.5 Mulinia lateralis (M) 1 0.3 0.6 6 6.5 Ilyanassa obsoleta (M) 1 0.3 0.6 6 6.5 Glycera americana (P) 1 0.3 0.6 6 6.5 ------------------------------------- Collection Date 30 January 1978 ---------------------------------- Lumbrineris tenuis (P) 6 2.0 2.0 36 1.0 Ilyanassa obsoleta (M) 4 1.3 1.5 24 2.5 Heteromastus filiformis (P) 4 1.3 0.6 24 2.5 Glycera americana (P) 2 0.7 1.2 12 5.0 Aricidea fragilis (P) 2 0.7 0.6 12 5.0 Haploscoloplos sp. (P) 2 0.7 0.6 12 5.0 Cyathura polita (1) 1 0.3 0.6 6 8.5 Mercenaria mercenaria (M) 1 0.3 0.6 6 8.5 Mulinia lateralis (M) 1 0.3 0.6 6 8.5 Nereis succinea (P) 1 0.3 0.6 6 8.5 ------------------------------------- Collection Date 25 April 1978 ----------------------------------- Haploscoloplos fragilis (P) 27 9.0 10.4 164 1.0 Lumbrineris tenuis (P) 17 5.7 6.4 103 2.0 Aricidea fragilis (P) 8 2.7 2.3 48 3.0 Streblospio benedicti (P) 3 1.0 1.0 18 4.0 Glycera americana (P) 2 0.7 0.6 12 5.5 Mediomastus californiensis (P) 2 0.7 1.2 12 5.5 Edotea montosa (1) 1 0.3 0.6 6 8.0 Heteromastus filiformis (P) 1 0.3 0.6 6 8.0 Nereis succinea (P) 1 0.3 0.6 6 8.0 ------------------------------------- Collection Date 24 July 1978 ------------------------------------ Mulinia lateralis (M) 1 0.3 0.6 6 3.0 Glycera americana (P) 1 0.3 0.6 6 3.0 Heteromastus filiformis (P) 1 0.3 0.6 6 3.0 Drilonereis magna (P) 1 0.0 0.0 6 3.0 Aricidea fragilis (P) 1 0.3 0.6 6 3.0 36 Table 21. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB07. (A Amphipoda; C = Cumacea; D = Decapoda; I = Isopoda; M = Mollusca; 0 = Ophiuroidea; P = Polychaeta; S = Stomatopoda). SB07 Rank Total Number/0.05m 2 Estimated by Species Number 3@ SD Number/m2 Number ------------------------------------ Collection Date 25 August 1977 ------------------------------------ Nereis succinea (P) 7 2.3 2.1 42 1.0 Glycera americana (P) 4 1.3 1.5 24 2.0 Lumbrineris tenuis (P) 3 1.0 1.0 18 3.0 Scoloplos rubra (P) 2 0.7 1.2 12 4.5 Tharyx marioni (P) 2 0.7 0.6 12 4.5 Alpheus normanni (D) 1 0.3 0.6 6 9.5 Batea catharinensis (A) 1 0.3 0.6 6 9.5 Hemipholis elongata (0) 1 0.3 0.6 6 9.5 Zrepidula fornicata (M) 1 0.3 0.6 6 9.5 Notomastus lobatus (P) 1 0.3 0.6 6 9.5 Glycinde solitaria (P) 1 0.3 0.6 6 9.5 Arabella iricolor (P) 1 0.3 0.6 6 9.5 Drilonereis magna (P) 1 0.3 0.6 6 9.5 ------------------------------------ Collection Date 30 January 1978 ----------------------------------- Mulinia lateralis (M) 10 3.3 3.5 61 1.0 Nereis succinea (P) 5 1.7 1.5 30 2.0 Paraprionos2io pinnata (P) 4 1.3 1.5 24 3.0 Glycera americans (P) 3 1.0 1.0 18 4.0 Xanthidae (undet.) (D) 2 0.7 1.2 12 7.0 Ampelisca vadorum (A) 2 0.7 0.6 12 7.0 Cyathura polita (1) 2 0.7 1.2 12 7.0 Streblospio benedicti (P) 2 0.7 1.2 12 7.0 Cirratulidae (undet.) (P) 2 0.7 1.2 12 7.0 Palaemonetes vulgaris (D) 1 0.3 0.6 6 18.5 Upogebia affinis (D) 1 0.3 0.6 6 18.5 Gammaridae (undet.) (A) 1 0.3 0.6 6 18.5 Melitidae (undet.) (A) 1 0.3 0.6 6 18.5 Nemertina sp. A 1 0.3 0.6 6 18.5 Nemertina sp. B 1 0.3 0.6 6 18.5 Mitrella lunata (M) 1 0.3 0.6 6 18.5 Macoma sp. (M) 1 0.3 0.6 6 18.5 Lumbrineris tenuis (P) 1 0.3 0.6 6 18.5 Glycinde solitaria (P) 1 0.3 0.6 6 18.5 Marphysa sanguinea (P) 1 0.3 0.6 6 18.5 Arabella -iricolor (P) 1 0.3 0.6 6 18.5 Haploscoloplos fragilis (P) 1 0.3 0.6 6 18.5 Oligochaeta (undet.) 1 0.3 0.6 6 18.5 Aricidea fragilis (P) 1 0.3 0.6 6 18.5 Lysidice ninetta (P) 1 0.3 0.6 6 18.5 Subadyte pellucida (P) 1 0.3 0.6 6 18.5 Pholoe minuta (P) 1 0.3 0.6 6 18.5 --7 ---------------------------------- Collection Date 24 April 1978 ------------------------------------ Ampelisca vadorum (A) 12 4.0 2.0 73 1.5 Lumbrineris tenuis (P) 12 4.0 2.0 73 1.5 Oxyurostylis smithi (C) 11 3.7 4.0 67 3.0 Glycera americana (P) 4 1.3 1.2 24 4.5 Nereis succinea (P) 4 1.3 0.6 24 4.5 Drilonereis magna (P) 3 1.0 1.0 18 6.0 Xanthidae (undet.) (D) 2 0.7 0.6 12 8.5 Gammaridae (undet.)(A) 2 0.7 1.2 12 8.5 Nemertina (undet.) 2 0.7 0.6 12 8.5 Haploscoloplos sp. (P) 2 0.7 0.6 12 8.5 Pagurus longicarpus (D) 1 0.3 0.6 6 17.5 Squilla empusa (S) 1 0.3 0.6 6 17.5 Caprella equilibra (A) 1 0.3 0.6 6 17.5 Nucula proxima (M) 1 0.3 0.6 6 17.5 Mercenaria mercenaria (M) 1 0.3 0.6 6 17.5 Abra aegualis (M) 1 0.3 0.6 6 17.5 Pelecypoda (undet.) (M) 1 0.3 0.6 6 17.5 Acteocina canaliculata (M) 1 0.3 0.6 6 17.5 Tellinidae (undet.) (M) 1 0.3 0.6 6 17.5 37 Table 21. (Cont. SB07 Rank Total Number/0.05m2 Estimatel by Species Number -9 SD Number/m Number Scoloplos rubra (P) 1 0.3 0.6 6 17.5 Pectinaria gouldii (P) 1 0.3 0.6 6 17.5 Scoloplos sp. (P) 1 0.3 0.6 6 17.5 Paraprionospio pinnata (P) 1 0.3 0.6 6 17.5 Mediomastus californiensis (P) 1 0.3 0.6 6 17.5 ------------------------------------- Collection Date 17 August 1978 ------------------------------------ Lumbrineris tenuis (P) 15 5.0 1.0 91 1.0 Panopeus herbstii (D) 6 2.0 1.0 36 2.0 Podarke obscura (P) 4 1.3 1.2 24 3.0 Cyathura buri@anki (1) 3 1.0 1.0 18 5.0 Heteromastus filiformis (P) 3 1.0 1.0 18 5.0 Aricidea fragilis (P) 3 1.0 1.0 18 5.0 Melita sp. (A) 2 0.7 0.6 12 9.0 Drilonereis magna (P) 2 0.7 0.6 12 9.0 Lepidonotus sublevis (P) 2 0.7 0.6 12 9.0 Diplocirrus capensis (P) 2 0.7 0.6 12 9.0 Cirratulidae (undet.).(P) 2 0.7 1.2 12 9.0 Alpheus normanni (D) 1 0.3 0.6 6 15.5 Nucula proxima (M) 1 0.3 0.6 6 15.5 Glycera americana (P) 1 0.3 0.6 6 15.5 Scoloplos rubra (P) 1 0.3 0.6 6 15.5 Nereis succinea (P) 1 0.3 0.6 6 15.5 Glycinde solitaria (P) 1 0.3 0.6 6 15.5 Arabella iricolor (P) 1 0.3 0.6 6 15.5 Syllis spongicola (P) 1 0.3 0.6 6 15.5 38 Table 22. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB08. (A Amphipoda; C = Cumacea; D = Decapoda; H = Hemichordata; I = Isopoda; M = Mollusca; 0 = Ophiuroidea; P = Polychaeta). SBO8 2 Rank Total Number/0.05m Estimated by Species Number -x SD Number/m2 Number ----------------------------------- Collection Date 25 August 1977 ------------------------------------ Lumbrineris tenuis (P) 6 2.0 2.0 36 1.5 Paraprionospio pinnata (P) 6 2.0 2.7 36 1.5 Glycera americana (P) 3 1.0 0.0 18 3.5 Scoloplos rubra (P) 3 1.0 1.0 18 3.5 Cyathura burbanki (1) 1 0.3 0.6 6 7.0 Hemipholis elongata (0) 1 0.3 0.6 6 7.0 Saccoglossus kowalevskii (H) 1 0.3 0.6 6 7.0 Gly@,@ solitaria (P) 1 0.3 0.6 6 7.0 Drilonereis magna (P) 1 0.3 0.6 6 7.0 ----------------------------------- Collection Date 30 January 1978 ---------------------------------- Paraprionospio pinnata (P) 11 3.7 4.7 67 1.0 Mulinia lateralis 7 2.3 2.5 42 2.0 Lumbrineris tenuis (P) 6 2.0 1.7 36 3.0 Nereis succinea (P) 5 1.7 0.6 30 4.5 Haploscoloplos robustos (P) 5 1.7 0.6 30 4.5 Heteromastus filiformis (P) 4 1.3 1.2 24 6.0 Ogyrides limicola (D) 3 1.0 1.7 18 7.5 Mitrella lunata (M) 3 1.0 1.0 18 7.5 Pinnixa sp. (D) 2 0.7 1.2 12 11.0 Ampelisca vadorum (A) 2 0.7 0.6 12 11.0 Cyathura burbanki (1) 2 0.7 1.2 12 11.0 Tellinidae (undet.) (M) 2 0.7 1.2 12 11.0 Lysidice ninetta (P) 2 0.7 1.2 12 11.0 Mercenaria mercenaria (M) 1 0.3 0.6 6 16.0 Glycera americana (P) 1 0.3 0.6 6 16.0 Glycinde solitaria (P) 1 0.3 0.6 6 16.0 Oligochaeta (undet.) 1 0.3 0.6 6 16.0 Polydora sp. (P) 1 0.3 0.6 6 16.0 ------------------------------------ Collection Date 24 April 1978 ----------------------------------- Haploscoloplos fragilis (P) 36 12.0 9.0 218 1.0 Ampelisca vadorum (A) 12 4.0 1.0 73 2.0 Spionidae (undet.) (P) 6 2.0 2.0 36 3.0 Heteromastus filiformis (P) 5 1.7 2.1 30 4.5 Lunbrineris tenuis (P) 5 1.7 0.6 30 4.5 Tellinidae (undet.) (M) 4 1.3 1.2 24 6.0 Melita nitida (A) 3 1.0 1.7 18 8.0 Nereis succinea (P) 3 1.0 1.7 18 8.0 GlyS_@ solitaria (P) 3 1.0 1.0 18 8.0 Leucon americanus (C) 2 0.7 0.6 12 10.0 Xanthidae (undet.) (D) 1 0.3 0.6 6 14.5 Nucula proxima (M) 1 0.3 0.6 6 14.5 Pelecypoda (undet.) (M) 1 0.3 0.6 6 14.5 Glycera americana (P) 1 0.3 0.6 6 14.5 Tharyx marioni (P) 1 0.3 0.6 6 14.5 Drilonereis magna (P) 1 0.3 0.6 6 14.5 Eteone heteropoda (P) 1 0.3 0.6 6 14.5 Tharyx setigera (P) 1 0.3 0.6 6 14.5 ------------------------------------ Collection Date 3 August 1978 ----------------------------------- Ogyrides limicola (D) 33 11.0 8.0 200 1.0 Haploscoloplos fragilis (P) 6 2.0 2.7 36 2.0 Lurrbrineris tenuis (P) 5 1.7 1.2 30 3.0 Paraprionospio pinnata (P) 3 1.0 1.7 18 4.0 Glycera americana (P) 1 0.3 0.6 6 5.5 Not3mastus sp. 1 0.3 0.6 6 5.5 39 Table 23. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB09. (A = Amphipoda; H = Hemichordata; I = Isopoda; M = Mollusca; P = Polychaeta; Py = Pycnogonida). SB09 Rank Total Number/0.05m2 Estimated by Species Number x SD Number/M2 Number ------------------------------------ Collection Date 23 August 1977 ------------------------------------ Lumbrineris tenuis (P) 49 16.3 11.6 297 1.0 Paraprionospio pinnata (P) 26 8.7 14.2 158 2.0 Aricidea fragilis (P) 14 4.7 3.1 85 3.0 Sacoglossus kowalevskii (H) 6 2.0 1.7 36 4.0 Mulinia lateralis (M) 5 1.7 1.2 30 5.5 Glycinde solitaria (P) 5 1.7 1.5 30 5.5 Glycera americana (P) 3 1.0 1.0 18 7.0 Heteromastus filiformis (P) 2 0.7 1.2 12 9.0 Haploscoloplos fragilis (P) 2 0.7 0.6 12 9.0 Haploscoloplos foliosus (P) 2 0.7 1.2 12 9.0 ------------------------------------ Collection Date 31 January 1978 ----------------------------------- Mulinia lateralis (M) 74 24.7 11.9 449 1.0 Lumbrineris tenuis (P) 19 6.3 9.3 115 2.0 Edotea montosa (1) 5 1.7 2.9 30 4.5 Odostomia sp. (P) 5 1.7 2.9 30 4.5 Heteromastus filiformis (P) 5 1.7 2.9 30 4.5 Haploscoloplos sp. (P) 5 1.7 2.1 30 4.5 Nereis succinea (P) 4 1.3 2.3 24 7.0 Glycera americana (P) 3 1.0 1.0 18 8.0 Tellinidae -(undet.) (M) 2 0.7 0.6 12 10.5 Eteone heteropoda (P) 2 0.7 0.6 12 10.5 Mediomastus californiensis (P) 2 0.7 0.6 12 10.5 Aricidea fragilis (P) 2 0.7 1.2 12 10.5 Paraphoxus spinosus (A) 1 0.3 0.6 6 20.0 Gammarus mucronatus (A) 1 0.3 0.6 6 20.0 Tanystylum calicirostre (PY) 1 0.3 0.6 6 20.0 Actinaria (undet.) 1 0.3 0.6 6 20.0 Polinices lacteus (M) 1 0.3 0.6 6 20.0 Mercenaria mercenaria (M) 1 0.3 0.6 6 20.0 Acteocina canaliculata (M) 1 0.3 0.6 6 20.0 Streblospio benedicti (P) 1 0.3 0.6 6 20.0 Marphysa sanguinea (P) 1 0.3 0.6 6 20.0 Drilonereis magna (P) 1 0.3 0.6 6 20.0 Leptdonotus sublevis (P) 1 0.3 0.6 6 20.0 Polydora ligni (P) 1 0.3 0.6 6 20.0 Paraprionospio pinnata (P) 1 0.3 0.6 6 20.0 Thelepus setosus (P) 1 0.3 0.6 6 20.0 Nereinides unidentata (P) 1 0.3 0.6 6 20.0 ------------------------------------- Collection Date 25 April 1978 -------------------------------------- Lumbrineris tenuis (P) 51 17.0 10.0 309 1.0 Haploscoloplos fragilis (P) 21 7.0 4.0 127 2.0 Heteromastus filiformis (P) 16 5.3 4.5 97 3.0 Streblospio benedicti (P) 12 4.0 5.3 73 4.5 Cirratulidae (undet.) (P) 12 4.0 4.6 73 4.5 Tellinidae (undet.) (M) 7 2.3 3.2 42 6.0 Aricidea fragilis (P) 5 1.7 0.6 30 7.0 Glycera americana (P) 3 1.0 1.0 18 8.0 Glycinde solitaria (P) 2 0.7 1.2 12 10.0 Oligochaeta (undet.) 2 0.7 1.2 12 10.0 Clymenella torquata (P) 2 0.7 1.2 12 10.0 Ampelisca vadorum (A) 1 0.3 0.6 6 13.5 Edotea montosa (1) 1 0.3 0.6 6 13.5 Nemertina (undet.) 1 0.3 0.6 6 13.5 Eteone heteropoda (P) 1 0.3 0.6 6 13.5 ------------------------------------- Collection Date 24 July 1978 -------------------------------------- Lumbrineris tennis (P) 12 4.0 3.0 73 1.0 Glycera americana (P) 3 1.0 1.0 18 2.5 Aricidea fragilis (P) 3 1.0 1.0 18 2.5 Cyathura burbanki (1) 1 0.3 0.6 6 5.5 Nemertina (undet.) 1 0.3 0.6 6 5.5 Mulinia lateralis (M) 1 0.3 0.6 6 5.5 Glycinde solitaria (P) 1 0.3 0.6 6 5.5 Table24,. Macroinvertebrate species collected from the Sewee Bay channel station, SB10. (A = Amphipoda; C = Cumacea; D = Decapoda; H = Hemicordata; M = Mollusca; P = Polychaeta). SB10 2 Rank Total Number/0.05m Estimate5 by Species Number -:w SD Number/m Number ------------------------------------ Collection Date 23 August 1977 ------------------------------------ Paraprionospio pinnata (P) 43 14.3 11.9 261 1.0 Lumbrineris tenuis (P) 10 3.3 1.2 61 2.0 Ogyrides limicola (D) 8 2.7 1.2 48 3.0 Notomastus lobatus (P) 5 1.7 1.5 30 4.0 Caprella equilibra (A) 3 1.0 1.7 18 5.5 Glycinde solitaria (P) 3 1.0 1.0 18 5.5 Batea catharinensis (A) 2 0.7 1.2 12 8.0 Glycera americana (P) 2 0.7 0.6 12 8.0 Tharyx.annulosus (P) 2 0.7 1.2 12 8.0 Alpheus heterochaelis (D) 1 0.3 0.6 6 11.5 Ampelisca vadorum (A) 1 0.3 0.6 6 11.5 Sacoglossus kowalevskii (H) 1 0.3 0.6 6 11.5 Maldanidae (undet.) (P) 1 0.3 0.6 6 11.5 ------------------------------------ Collection Date 30 January 1978 ----------------------------------- Ogyrides limicola (D) 8 2.7 1.5 48 1.0 Heteromastus.filiformis (P) 2 0.7 1.2 12 2.5 Paraprionospio pinnata (P) 2 0.7 0.6 12 2.5 Leucon americanus (C) 1 0.3 0.6 6 4.5 Abra aegualis (M) 1 0.3 0.6 6 4.5 ------------------------------------- Collection Date 28 April 1978 ------------------------------------ Heteromastus filiformis (P) 67 22.3 5.5 406 1.0 Paraprionospio pinnata (P) 20 6.7 1.5 121 2.0 Gemma gemma (M) 12 4.0 6.1 73 3.5 Nereis succinea (P) 12 4.0 3.6 73 3.5 Haploscoloplos fragilis .(P) 11 3.7 3.2 67 5.0 Ogyrides limicola (D) 9 3.0 3.6 55 6.0 Lumbrineris tenuis (P) 6 2.0 2.0 36 8.5 @rilonereis magna (P) 6 2.0 1.0 36 8.5 Clymenella torquata (P) 6 2.0 2.0 36 8.5 Streblospio benedicti (P) 6 2.0 2.0 36 8.5 Tellinidae (undet.) (M) 5 1.7 1.5 30 11.0 Mulinia lateralis (M) 4 1.3 0.6 24 12.5 Nereidae (undet.) (P) 4 1.3 1.5 24 12.5 Ampelisca vadorum (A) 3 1.0 0.0 18 15.5 Nemertina (undet.) 3 1.0 1.0 18 15.5 Haploscoloplos fragilis (P) 3 1.0 0.0 18 15.5 Aricidea fragilis (P) 3 1.0 0.0 18 15.5 Oxyurostylis smithi (C) 2 0.7 1.2 12 19.0 Polinices lacteus (M) 2 0.7 0.6 12 19.0 Mediomastus californiensis (P) 2 0.7 1.2 12 19.0 Solen viridis (M) 1 0.3 0.6 6 24.0 Abra aequalis (M) 1 0.3 0.6 6 24.0 Pelecypoda. (undet.) (M) 1 0.3 0.6 6 24.0 Tellinidae (undet.) (M) 1 0.3 0.6 6 24.0 Glycera americana (P) 1 0.3 0.6 6 24.0 Pectinaria gouldii (P) 1 0.3 0.6 6 24.0 Cirratulidae (undet.) (P) 1 0.3 0.6 6 24.0 ------------------------------------- Collection Date 3 August 1978 ----------------------------------- Ogyrides limicola (D) 64 21.3 4.0 388 1.0 Heteromastus filiformis (P) 24 8.0 3.6 145 2.0 Haploscoloplo's fragilis (P) 19 6.3 3.1 115 3.5 Paraprionospio pinnata (P) 19 6.3 6.8 115 3.5 Glycera. americans (P) 2 0.7 0.6 12 6.0 Nereis succinea (P) 2 0.7 1.2 12 6.0 Glycfnde solitaria (P) 2 0.7 1.2 12 6.0 Pinnixa sayana (D) 1 0.3 0.6 6 10.0 Sigambra tentaculata (P) 1 0.3 0.6 6 10.0 Lumbrineris tenuis (P) 1 0.3 0.6 6 10.0 Diopatra cuprea (P) 1 0.3 0.6 6 10.0 Oligochaeta (undet.) 1 0.3 0.6 6 10.0 41 Table25. Macroinvertebrate species collected from the Sewee Bay intertidal station, SB11. (M Mollusca; P = Polychaeta). SBII Rank Total Number/0.05m 2 Estimated by Species Number -K SD Number/m2 Number ----------------------------------- Collection Date 30 August 1977 ---------------------------------- Heteromastus filiformis (P) 91 30.3 13.8 552 1.0 Nereis succinea (P) 37 12.3 10.4 224 2.0 Gemma gemma (M) 11 3.7 1.5 67 3.0 Aricidea fragilis (P) 10 3.3 4.9 61 4.0 Lumbrineris tenuis (P) 6 2.0 3.5 36 5.0 Laeonereis culveri (P) 3 1.0 1.0 18 6.0 Glycera americana (P) 1 0.3 0.6 6 8.0 Diopatra cuprea (P) 1 0.3 0.6 6 8.0 Drilonereis magna (P) 1 0.3 0.6 6 8.0 ---------------------------------- Collection Date 10 February 1978 --------------------------------- Heteromastus filiformis (P) 47 15.7 10.1 285 1.0 Gemma gemma (M) 42 14.0 13.2 255 2.0 Paraprionospio pinnata (P) 16 5.3 5.5 97 3.0 Nereidae (undet.) (P) 5 1.7 1.2 30 4.0 Lumbrineris tenuis (P) 2 0.7 1.2 12 5.0 Mercenaria mercenaria (M) 1 0.3 0.6 6 8.5 Tagelus plebeius (P) 1 0.3 0.6 6 8.5 Glycera americana (P) 1 0.3 0.6 6 8.5 Nereis succinea (P) 1 0.3 0.6 6 8.5 Diopatra cuprea (P) 1 0.3 0.6 6 8.5 Haploscoloplos sp. (P) 1 0.3 0.6 6 8.5 ------------------------------------ Collection Date 28 April 1978 ---------------------------------- Heteromastus filiformis (P) 51 17.0 6.1 309 1.0 Gemma gemma. (M) 12 4.0 6.1 73 2.5 Nereis succinea (P) 12 4.0 3.6 73 2.5 Haploscoloplos fragilis (P) 11 3.7 3.2 67 4.0 Lumbrineris tenuis (P) 6 2.0 2.0 36 5.5 Drilonereis magna (P) 6 2.0 1.0 36 5.5 Nereidae (undet.) (P) 4 1.3 1.5 24 7.0 Nemertina (undet.) 3 1.0 1.0 18 8.5 Aricidea fragilis (P) 3 1.0 0.0 18 8.5 Polinices lacteus (M) 2 0.7 0.6 12 10.5 Streblospio benedicti (P) 2 0.7 1.2 12 10.5 Tellinidae (undet.) (M) 1 0.3 0.6 6 12.0 ----------------------------------- Collection Date 18 August 1978 ---------------------------------- Nereis succinea (P) 48 16.0 8.7 291 1.0 Heteromastus filiformis (P) 24 8.0 6.1 145 2.0 Gemma gemma (M) 19 6.3 1.5 115 3.0 Haploscoloplos fragilis (P) 18 6.0 4.4 109 4.0 Aricidea fragilis (P) 3 1.0 1.0 18 5.0 Nemertina (undet.) 1 0.3 0.6 6 7.0 Lumbrineris tenuis (P) 1 0.3 0.6 6 7.0 Drilonereis magna (P) 1 0.3 0.6 6 7.0 42 Table 26. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB12. (A = Amphipoda; I = Isopoda; M = Mollusca; P = Polychaeta). SB12 Rank Total Number/0.05m2 Estimated by Species Number T SD Number/M2 Number ---------------------------------------- Collection Date = 30 August 1977 -------------------------------- Haploscoloplos robustos (P) 41 13.7 3.8 249 1.0 Lumbrineris tenuis (P) 11 3.7 3.8 67 2.0 Heteromastus filiformis (P) 9 3.0 2.7 55 3.0 Aricidea fragilis (P) 8 2.7 3.1 48 4.0 Cyathura burbanki (1) 1 0.3 0.6 6 5.5 Streblospio benedic-ti (P) 1 0.3 0.6 6 5.5 ---------------------------------------- Collection Date = 31 January 1978 ------------------------------- Nereis succinea (P) 34 11.3 7.1 206 1.0 Heteromastus filiformis (P) 18 6.0 3.0 109 2.0 Paraprionospio pinnata (P) 13 4.3 4.0 79 3.0 Haploscoloplos fragilis (P) 6 2.0 1.0 36 4.0 Glycera americana (P) 3 1.0 1.0 18 5.5 Nereidae (undet.) (P) 3 1.0 1.0 18 5.5 Mulinia lateralis (M) 1 0.3 0.6 6 8.0 Tellinidae (undet.) (M) 1 0.3 0.6 6 8.0 Oligochaeta (undet.) 1 0.3 0.6 6 8.0 ----------------------------------------- Collection Date = 25 April 1978 -------------------------------- Haploscoloplos fragilis (P) 21 7.3 9.3 127 1.0 Streblospio benedicti (P) 18 5.0 8.7 109 2.0 Mediomastus californiensis (P) 10 3.3 3.2 61 3.0 Heteromastus filiformis (P) 8 2.7 1.2 48 4.0 Paraprionospio pinnata (P) 4 1.3 1.5 24 5.0 Lumbrineris tenuis (P) 3 1.0 1.7 18 6.0 Ampelisca vadorum (A) 2 0.7 1.2 12 7.5 Glycera americana (P) 2 0.7 0.6 12 7.5 Ogyrides limicola (D) 1 0.3 0.6 6 12.5 Ilyanassa obsoleta (M) 1 0.3 0.6 6 12.5 Tellinidae (undet.) (M) 1 0.3 0.6 6 1.2.5 Nereis succinea (P) 1 0.3 0.6 6 12.5 Eteone heteropoda (P) 1 0.3 0.6 6 12.5 Oligochaeta (undet.) 1 0.3 0.6 6 12.5 Aricidea fragilis (P) 1 0.3 0.6 6 12.5 Cirratulidae (undet.) (P) 1 0.3 0.6 6 12.5 ---------------------------------------- Collection Date 18 August 1978 ------------------------------- Haploscoloplos fragilis (P) 24 8.0 7.6 145 1.0 Heteromastus filiformis (P) 8 2.7 1.5 48 2.0 Paraprionospio pinnata (P) 5 1.7 1.5 30 3.0 Lumbrineris tenuis (P) 3 1.0 0.0 18 4.0 Oligochaeta (undet.) 2 0.7 0.6 12 5.0 Sigambra tentaculata (P) 1 0.3 0.6 6 7.0 Glycinde solitaria (P) 1 0.3 0.6 6 7.0 Aricidea fragilis (P) 1 0.3 0.6 6 7.0 43 Table 27. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB13. (A = Amphipoda; C = Cumacea; D = Decapoda; Ho @ Holothuroidea; I = Isopoda; M = Mollusca; P = Polychaeta). SB13 Rank Total Number/0.05m2 Estimatel by Species Number -9 SD Number/m Number ----------------------------------- Collection Date 30 August 1977 ---------------------------------- Lumbrineris tenuis (P) 42 14.0 23.4 255 1.0 Ogyrides limicola (D) 6 2.0 2.0 36 2.0 Nereis succinea (P) 2 0.7 1.2 12 3.0 Sclerodactyla briareus (HO) 1 0.3 0.6 6 5.5 Glycera americans (P) 1 0.3 0.6 6 5.5 Heteromastus filiformis (P) 1 0.3 0.6 6 5.5 Diopatra cuprea (P) 1 0.3 0.6 6 5.5 ----------------------------------- Collection Date 30 January 1978 --------------------------------- Mulinia lateralis (M) 9 3.0 1.7 55 1.0 Heteromastus filiformis (P) 3 1.0 1.0 18 2.5 Lumbrineris tenuis (P) 3 1.0 1.0 18 2.5 Nucula proxima. (M) 2 0.7 1.2 12 4.0 Edotea montosa (1) 1 0.3 0.6 6 8.0 Pelecypoda (undet.) (M) 1 0.3 0.6 6 8.0 Nereis succinea (P) 1 0.3 0.6 6 8.0 Lepidonotus sublevis (P) 1 0.3 0.6 6 8.0 Paraprionospio pinnata (P) 1 0.3 0.6 6 8.0 Sabellidae (undet.) (P) 1 0.3 0.6 6 8.0 Sabella microphthalma (P) 1 0.3 0.6 6 8.0 ------------------------------------ Collection Date 24 April 1978 ---------------------------------- Ampelisca vadorum (A) 42 14.0 4.4 255 1.0 Lumbrineris tenuis (P) 13 4.3 1.5 79 2.0 Haploscoloplos fragilis (P) 12 4.0 3.0 73 3.0 Leucon americanus (C) 4 1.3 1.5 24 4.0 Glycinde solitaria (P) 3 1.0 1.0 18 5.0 Ogyrides limicola (D) 2 0.7 0.6 12 7.0 Oxyurostylis smithi (C) 2 0.7 0.6 12 7.0 Paraprionospio pinnata (P) 2 0.7 0.6 12 7.0 Mulinia lateralis (M) 1 0.3 0.6 6 10.5 Turridae (undet.) (M) 1 0.3 0.6 6 10.5 Glycera americana (P) 1 0.3 0.6 6 10.5 Drilonereis magna (P) 1 0.3 0.6 6 10.5 ------------------------------------ Collection Date 17 July 1978 ----------------------------------- Glycinde solitaria (P) 8 2.7 1.5 48 1.0 Haploscoloplos fragilis (P) 7 2.3 3.2 42 2.0 Paraprionospio pinnata (P) 3 1.0 0.0 18 3.0 Ogyrides limicola (D) 1 0.3 0.6 6 6.0 Callianassa atlantica (D) 1 0.3 0.6 6 6.0 Glycera ame'ricana (P) 1 0.3 0.6 6 6.0 Sigambra tentaculata (P) 1 0.3 0.6 6 6.0 Lumbrineris tenuis (P) 1 0.3 0.6 6 6.0 44 Table 28. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB14. (A Amphipoda; C = Cumacea; D = Decapoda; I = Isopoda; M = Mollusca: P = Polychaeta). SB14 Rank Total Number/0.05m2 Estimated by Species Number x SD Number/m2 Number ------------------------------------ Collection Date 23 August 1977 ------------------------------------ Paraprionospio pinnata (P) 52 17.3 17.9 315 1.0 Tumbrineris tenuis (P) 10 3.3 4.9 61 2.0 Glycinde solitaria (P) 4 1.3 2.3 24 3.0 Periclimenes longicaudatus (D) 3 1.0 1.7 18 4.5 Rereis succinea (P) 3 1.0 1.7 18 4.5 Haploscoloplos fragilis (P) 2 0.7 1.2 12 6.0 fanopeus herbst@ii -(D) 1 0.3 0.6 6 9.0 Melita nitida (A) 1 0.3 0.6 6 9.0 Paraphoxus oculatus (A) 1 0.3 0.6 6 9.0 Mulinia lateralis (M) 1 0.3 0.6 6 9.0 Heteromastus filiformis (P) 1 0.3 0.6 6 9.0 ------------------------------------ Collection Date 31 January 1978 ----------------------------------- Streblospio benedictii (P) 58 19.0 19.1 352 1.0 Sabellaria vulgaris (P) 43 14.3 22.2 261 2.0 Lumbrineris tenuis (P) 21 7.0 2.7 127 3.0 Heteromastus filiformis (P) 8 2.7 2.1 48 4.0 Rulinia lateralis (M) 5 1.7 2.1 30 5.0 Eteone heteropoda (P) 4 1.3 1.5 24 6.0 Ampelisca vadorum (A) 3 1.0 0.0 18 9.0 Macoma sp. (M) 3 1.0 1.0 18 9.0 Tharyx marioni (P) 3 1.0 1.7 18 9.0 Nereis succinea (P) 3 1.0 1.7 18 9.0 -@araprionospio pinnata (P) 3 1.0 1.0 18 9.0 Melita nitida @A) 2 0.7 0.6 12 12.5 Leucon americanus (C) 2 0.7 1.2 12 12.5 Callinectes sapidus (D) 1 0.3 0.6 6 17.5 Caprella equilibra (A) 1 0.3 0.6 6 17.5 Corophium sp. (A) 1 0.3 0.6 6 17.5 Glycera americana (P) 1 0.3 0.6 6 17.5 Scoloplos rubra (P) 1 0.3 0.6 6 17.5 Drilonereis magna (P) 1 0.3 0.6 6 17.5 Thelepus setosus (P) 1 0.3 0.6 6 17.5 -§abella microphthalma (P) 1 0.3 0.6 6 17.5 ------------------------------------- Collection Date 25 April 1978 ------------------------------------ Lumbrineris tenuis (P) 33 11.0 5.3 200 1.0 Ampelisca vadorum (A) 14 4.7 1.2 85 2.5 Spiophanes bombyx (P) 14 4.7 5.7 85 2.5 Cirratulidae (undet.) (P) 11 3.7 4.7 67 4.0 Paraprionospi pinnata (P) 7 2.3 1.5 42 5.5 Mediomastus cafi7forniensis (P) 7 2.3 0.6 42 5.5 -@treblospio benedicti (P) 6 2.0 2.7 36 7.0 _KP-reis succinea (P) 4 1.3 2.3 24 8.0 Rucula proxima (M) 3 1.0 1.7 18 9.5 Heteromast us filiformis (P) 3 1.0 1.0 18 9.5 OLcyurostylis smithi (C) 2 0.7 1.2 12 11.5 Drilonereis magna (P) 2 0.7 0.6 12 11.5 Paguridea (undet.) (D) 1 0.3 0.6 6 21.5 UUca sp. (D) 1 0.3 0.6 6 21.5 Unciola serrata (A) 1 0.3 0.6 6 21.5 Edotea mo'ntosa (1) 1 0.3 0.6 6 21.5 Actinaria (undet.) 1 0.3 0.6 6 21.5 Nemertina (undet.) 1 0.3 0.6 6 21.5 Mercenaria mercenaria (M) 1 0.3 0.6 6 21.5 Iyonsia hyalina (M) 1 0.3 0.6 6 21.5 Acteocina canaliculata (M) 1 0.3 0.6 6 21.5 Tellinidae (undet.) M) 1 0.3 0.6 6 21.5 Sabellaria vulgaris (P) 1 0.3 0.6 6 21.5 Pectinaria gouldii (P) 1 0.3 0.6 6 21.5 Glycinde solitaria (P) 1 0.3 0.6 6 21.5 Diopatra cuprea (P) 1 0.3 0.6 6 21.5 Eteone heteropoda (P) 1 0.3 0.6 6 21.5 Exogone dispar (P) Thelepus setosus (P) 1 0.3 0.6 6 21.5 Haploscoloplos sp. (P) 1 0.3 0.6 6 21.5 0.3 0.6 6 21.5 Table 28.(Cont.) SB14 Rank Total Number/0.05m2 Estimated by Species Number -:w SD Number/m2 Number ------------------------------------ Collection Date 18 August 1978 ------------------------------------ Lumbrineris tenuis (P) 8 2.7 2.9 48 1.0 Heteromastus filiformis (P) .4 1.3 0.6 24 2.0 Marphysa sanguinea (P) 2 0.7 1.2 12 3.0 Nemertina (undet.) 1 0.3 0.6 6 5.0 Mercenaria mercenaria (M) 1 0.3 0.6 6 5.0 Mulinia lateralis (M) 1 0.3 0.6 6 5.0 46 Table 29. Macroinvertebrate species collected from the Sewee Bay channel station, SB15. (A Amphipoda; D = Decapoda; M = Mollusca; 0 = Ophiuroidea; P = Polychaeta). SB15 2 Rank Total Number/0.05m Estimated by Species Number -k SD Number/m 2 Number ----------------------------------- Collection Date 23 August 1977 ---------------------------------- Paraprionospio pinnata (P) 131 43.7 11.8 794 1.0 Glycinde solitaria (P) 10 3.3 2.1 61 2.0 Lumbrineris tenuis (P) 8 2.7 3.8 48 3.0 Ogyrides limicola (D) 1 0.3 0.6 6 7.0 Ampelisca verrilli (A) 1 0.3 0.6 6 7.0 Anadara ovalis (M) 1 0.3 0.6 6 7.0 Glycera americana (P) 1 0.3 0.6 6 7.0 Notomastus lobatus (P) 1 0.3 0.6 6 7.0 Scoloplos rubra (P) 1 0.3 0.6 6 7.0 Diopatra cuprep (P) 1 0.3 0.6 6 7.0 ----------------------------------- Collection Date 30 January 1978 --------------------------------- Paraprionospio pinnata (P) 9 3.0 3.6 55 1.0 Glycera americana (P) 3 1.0 1.7 18 2.5 Scoloplos rubra (P) 3 1.0 1.0 18 2.5 Streblospio benedicti (P) 2 0.7 1.2 12 4.0 Melita sp. (A) 1 0.3 0.6 6 7.5 Amphiuridae (undet.) (0) 1 0.3 0.6 6 7.5 Mulinia lateralis (M) 1 0.3 0.6 6 7.5 Heteromastus filiformis (P) 1 0.3 0.6 6 7.5 Oligochaeta (undet.) 1 0.3 0.6 6 7.5 Aricidea fragilis (P) 1 0.3 0.6 6 7.5 ------------------------------------ Collection Date 28 April 1978 ---------------------------------- Pelecypoda (undet.) (M) 4 1.3 2.3 24 1.0 Tellinidae (undet.) (M) 2 0.7 1.2 12 3.0 Haploscoloplos fragilis (P) 2 0.7 1.2 12 3.0 Clymenella torquata (P) 2 0.7 0.6 12 3.0 Ampelisca vadorum (A) 1 0.3 0.6 6 8.5 Erichthonius brasiliensis (A) 1 0.3 0.6 6 8.5 Glycera americana (P) 1 0.3 0.6 6 8.5 Streblospio benedicti (P) 1 0.3 0.6 6 8.5 Spiophanes bombyx (P) 1 0.3 0.6 6 8.5 Heteromastus filiformis (P) 1 0.3 0.6 6 8.5 Nereis succinea (P) 1 0.3 0.6 6 8.5 Paraprionospio pinnata (P) 1 0.3 0.6 6 8.5 ------------------------------------ Collection Date 31 July 1978 ----------------------------------- Paraprionospio pinnata (P) 18 6.0 2.7 109 1.0 Clymenella torquata (P) 3 1.0 1.7 18 2.0 Turbonilla sp. (M) 2 0.7 1.2 12 3.0 Pinnixa sayana (D) 1 0.3 0.6 6 6.0 Acteocina canaliculata (M) 1 0.3 0.6 6 6.0 Tellinidae (undet.) (M) 1 0.3 0.6 6 6.0 Glycera americana (P) 1 0.3 0.6 6 6.0 Glycinde solitaria (P) 1 0.3 0.6 6 6.0 47 Table 30. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB16. (D Decapoda; I = Isopoda; M = Mollusca; P = Polychaeta), SB16 Rank Total Number/0.05m2 Estimated by Species Number -:i SD Number/m2 Number ----------------------------------- Collection Date 30 August 1977 ------------------------------------- Lumbrineris tenuis (P) 36 12.0 7.6 218 1.0 Haploscoloplos fragilis (P) 13 4.3 4.2 79 2.0 Nereis succinea (P) 5 1.7 0.6 30 3.0 -Glycera americana (P) 4 1.3 2.3 24 4.0 Aricidea fragilis (P) 3 1.0 1.7 18 5.0 c@emma geuma -(M) 2 0.7 1.2 12 6.0 Cyathura-'@urbanki (1) 1 0.3 0.6 6 10.0 -Rercenaria mercenaria (M) 1 0.3 0.6 6 10.0 Tagelus divisus (M) 1 0.3 0.6 6 10.0 Rulinia lateralis (M) 1 0.3 0.6 6 10.0 Heteroma-stusfiliformis (P) 1 0.3 0.6 6 10.0 75rilonereis magna (P) 1 0.3 0.6 6 10.0 Maldanidae (-undet.) (P) 1 0.3 0.6 6 10.0 ---------------------------------- Collection Date 10 February 1978 ------------------------------------ Laeonereis culveri (P) 82 27.3 13.6 497 1.0 Nereis succinea (P) 44 14.7 11.0 267 2.0 Heteromastus filiformis (P) 25 8.3 5.5 152 3.0 Lumbrineris tenuis (P) 21 7.0 2.0 127 4.0 Glycera americana (P) 6 2.0 1.0 36 5.5 Eteone heteropoda (P) 6 2.0 2.7 36 5.5 Haploscoloplos sp. (P) 5 1.7 2.1 30 7.0 Macoma extenuata (M) 4 1.3 2.3 24 9.0 Paraprionospio pinnata (P) 4 1.3 1.5 24 9.0 Cirratulidae (undet.) (P) 4 1.3 2.3 24 9.0 Mercenaria mercenaria (M) 2 0.7 0.6 12 12.0 Mulinia lateralis (M) 2 0.7 0.6 12 12.0 -@treblospio benedicti (P) 2 0.7 1.2 12 12.0 Gemma gemma (M) 1 0.3 0.6 6 14.5 Pectinaria gouldii (P) 1 0.31 0.6 6 14.5 ------------------------------------ Collection Date 25 April 1978 ------------------------------------- Lumbrineris tenuis (P) 18 6.0 4.6 109 1.0 Heteromastus filiformis (P) 8 2.7 1.5 48 2.5 Mediomastus californiensis (P) 8 2.7 2.1 48 2.5 Streblospio benedicti (P) 7 2.3 2.5 42 4.5 Nereis succinea (P) 7 2.3 4.0 42 4.5 Uaploscoloplos-fragilis (P) 6 2.0 2.0 36 6.5 Paraprionospio pinnata (P) 6 2.0 1.0 36 6.5 Tellinidae (und-et.)(M) 4 1.3 1.5 24 8.5 Cirratulidae (undet.) (P) 4 1.3 2.3 24 8.5 Nemertina (undet.) 2 0.7 0.6 12 11.0 Mercenaria mercenaria (M) 2 0.7 0.6 12 11.0 dlycera americana (P) 2 0.7 0.6 12 11.0 Pinnixa sayana (D) 1 0.3 0.6 6 16.5 Gemma gemma (M) 1 0.3 0.6 6 16.5 Mulinia lateralis (M) 1 0.3 0.6 6 16.5 Acteocina canal-i-culata (M) 1 0.3 0.6 6 16.5 Scoloplos rubra (P) 1 0.3 0.6 6 16.5 Glycinde solitaria (P) 1 0.3 0.6 6 16.5 Drilonereis magna (P) 1 0.3 0.6 6 16.5 Notomastus sp. (P) 1 0.3 0.6 6 16.5 ----------------------------------- Collection Date 18 August 1978 ------------------------------------- Heteromastus filiformis (P) 38 12.7 21.9 230 1.0 Uca pugilator (D) 12 4.0 5.3 73 2.0 Lumbrineris tenuis (P) 6 2.0 3.5 36 3.0 Gemma gemma (M) 5 1.7 1.5 30 4.0 Nereis succinea (P) 4 1.3 1.5 24 5.0 Cirratulidae (undet.) (P) 2 0.7 1.2 12 6.0 Palaemonetes sp. (D) 1 0.3 0.6 6 7.0 48 Table 31. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB17. (A Amphipoda; C = Cumacea; D = Decapoda; Ho = Holothoroidea; I = Isopoda; M Mollusca; 0 = Ophiuroidea; P = Polychaeta). SB17 Rank Total Number/0.05m2 Estimate by Species Number _9 SD Number/m Number ---------------------------------- Collection Date 30 August 1977 ------------------------------------ Lumbrineris tenuis (P) 49 16.3 4.5 297 1.0 Caprella equilibra (A) 4 1.3 2.3 24 2.0 Glycera americana (P) 3 1.0 1.0 18 3.5 Nereis succinea (P) 3 1.0 1.0 18 3.5 Hemipholis elongata (0) 2 0.7 1.1 12 7.0 Macoma sp. (M) 2 0.7 1.1 12 7.0 Scoloplos rubra (P) 2 0.7 1.1 12 7.0 Arabella iricolor (P) 2 0.7 1.1 12 7.0 Aricidea fragilis (P) 2 0.7 0.6 12 7.0 Upogebia affinis (D) 1 0.3 0.6 6 13.5 Pagurus pollicaris (D) 1 0.3 0.6 6 13.5 Xanthidae (undet.) (D) 1 0.3 0.6 6 13.5 Sclerodactyla briareus (Ho) 1 0.3 0.6 6 13.5 Nucula proxima (M) 1 0.3 0.6 6 13.5 Eunice websteri (P) 1 0.3 0.6 6 13.5 Diopatra cuprea (P) 1 0.3 0.6 6 13.5 Drilonereis magna (P) 1 0.3 0.6 6 13.5 --------------------------------- Collection Date 10 February 1978 ----------------------------------- Haploscoloplos sp. (P) 11 3.7 1.5 67 1.0 Ogyrides limicola (D) 4 1.3 2.3 24 2.5 Ilyanassa obsoleta (M) 4 1.3 2.3 24 2.5 Lumbrineris tenuis (P) 3 1.0 1.0 18 5.0 Nereis succinea (P) 3 1.0 1.0 18 5.0 Paraprionospio pinnata (P) 3 1.0 1.0 18 5.0 Paraphoxus spinosus (A) 2 0.7 0.6 12 9.5 Ampelisca abdita (A) 2 0.7 1.2 12 9.5 Acteocina canaliculata (M) 2 0.7 1.2 12 9.5 Macoma extenuata (M) 2 0.7 1.2 12 9.5 Glycera americana (P) 2 0.7 0.6 12 9.5 Glycinde solitaria (P) 2 0.7 0.6 12 9.5 Corophium acherusicum (A) 1 0.3 0.6 6 16.0 Caprella equilibra (A) 1 0.3 0.6 6 16.0 Leucon americanus (C) 1 0.3 0.6 6 16.0 Edotea montosa (1) 1 0.3 0.6 6 16.0 Macoma sp. (M) 1 0.3 0.6 6 16.0 Laeonereis culveri (P) 1 0.3 0.6 6 16.0 Eteone heteropoda (P) 1 0.3 0.6 6 16.0 ----------------------------------- Collection Date 25 April 1978 ------------------------------------ Haploscoloplos fragilis (P) 17 6.0 5.0 103 1.0 Ampelisca vadorum (A) 9 3.0 1.0 55 2.0 Acteocina canaliculata (M) 5 1.7 1.2 30 3.5 Lumbrineris tenuis (PT 5 1.7 1.5 30 3.5 Tellinidae (undet.) (M) 4 1.3 1.5 24 5.0 Paraprionospio pinnata (P) 3 1.0 1.0 18 6.0 Glycera americana (P) 2 0.7 0.6 12 7.0 Ogyrides limicola (D) 1 0.3 0.6 6 11.0 Leucon americanus (C) 1 0.3 0.6 6 11.0 Heteromastus filiformis (P) 1 0.3 0.6 6 11.0 Glycinde solitaria (P) 1 0.3 0.6 6 11.0 Drilonereis magna (P) 1 0.3 0.6 6 11.0 Orbiniidae (undet.) (P) 1 0.3 0.6 6 11.0 Notomastus sp. (P) 1 0.3 0.6 6 11.0 ---------------------------------- Collection Date 17 August 1978 ------------------------------------ Glycera americana (P) 2 0.7 0.6 12 1.0 Lumbrineris tenuis (P) 1 0.3 0.6 6 2.0 49 Table 32. Macroinvertebrate species collected from the Sewee Bay subtidal station, SB18. A Amphipoda; C = Cumacea; D = Decapoda; I = Isopoda; M = Mollusca; My = Mysidacea; 0 = Ophiuroidea; P = Polychaeta; S = Stomatopoda). SB18 2 Rank Total Number/0.05m Estimated by Species Number -9 SD Number/m2 Number ------------------------------------ Collection Date 25 August 1977 ------------------------------------ Lumbrineris tenuis (P) 47 15.7 16.1 285 1.0 Glycinde solitaria (P) 3 1.0 0.0 18 2.0 Squilla empusa (S) 1 0.3 0.6 6 6.5 Ampel,isca vadorum (A) 1 0.3 0.6 6 6.5 Cyathura burbanki (1) 1 0.3 0.6 6 6.5 Scoloplos rubra (P) 1 0.3 0.6 6 6.5 Heteromastus filiformis (P) 1 0.3 0.6 6 6.5 Drilonereis magna (P) 1 0.3 0.6 6 6.5 Aricidea fragilis (P) 1 0.3 0.6 6 6.5 Syllidae (undet.) (P) 1 0.3 0.6 6 6.5 ------------------------------------ Collection Date 31 January 1978 ----------------------------------- Mulinia lateralis (M) 28 9.3 3.1 170 1.0 Paraprionospio pinnata (P) 22 7.3 4.7 133 2.0 Ogyrides limicola (D) 21 7.0 7.6 127 3.0 Paracaprella tenuis (A) 18 6.0 10.4 109 4.0 Erichthonius brasiliensis (A) 13 4.3 7.5 79 5.0 Tharyx marioni (P) 6 2.0 3.5 36 6.5 Heteromastus filiformis (P) 6 2.0 2.0 36 6.5 Lumbrineris tenuis (P) 5 1.7 2.1 30 8.0 Ampelisca vadorum (A) 4 1.3 1.5 24 10.0 Batea catharinensis (A) 4 1.3 2.3 24 10.0 Nereis succinea (P) 4 1.3 1.5 24 10.0 Microdeutopus gryllotalpa (A) 3 1.0 1.7 18 12.5 Oligochaeta (undet.) 3 1.0 1.0 18 12.5 Caprella equilibra (A) 2 0.7 1.2 12 15.0 Melita sp. (A) 2 0.7 1.2 12 15.0 Haploscoloplos robustos (P) 2 0.7 0.6 12 15.0 Pinnixa sp. (D) 1 0.3 0.6 6 22.5 Corophium acherusicum (A) 1 0.3 0.6 6 22.5 Leucon americanus (C) 1 0.3 0.6 6 22.5 Cyathura burbanki (1) 1 0.3 0.6 6 22.5 Abra aequalis (M) 1 0.3 0.6 6 22.5 Acteocina canaliculata (M) 1 0.3 0.6 6 22.5 Pectinaria gouldii (P) 1 0.3 0.6 6 22.5 Eteone heteropoda (P) 1 0.3 0.6 6 22.5 Odontosyllis fulgurans (P) 1 0.3 0.6 6 22.5 Aricidea fragilis (P) 1 0.3 0.6 6 22.5 Ampharetidae (undet.) (P) 1 0.3 0.6 6 22.5 Sabella microphthalma (P) 1 0.3 0.6 6 22.5 ------------------------------------- Collection Date 24 April 1978 ------------------------------------ Ampelisca vadorum (A) 23 7.7 1.5 139 1.0 Paraprionospio pinnata (P) 11 3.7 2.1 67 2.0 Lumbrineris tenuis (P) 7 2.3 1.5 42 3.0 Ogyrides limicola (D) 6 2.0 1.0 36 4.5 Spionidae (undet.) (P) 6 2.0 2.0 36 4.5 Neomysis americana (MY) 5 1.7 2.1 30 6.5 Tellinidae (undet.) (M) 5 1.7 1.5 30 6.5 Glycera americana (P) 4 1.3 1.2 24 9.0 Glycinde solitaria (P) 4 1.3 0.6 24 9.0 Haploscoloplos sp. (P) 4 1.3 0.6 24 9.0 Batea cathariensis (A) 2 0.7 1.2 12 14.0 Paracaprella tenuis (P) 2 0.7 1.2 12 14.0 Leucon americanus (C) 2 0.7 0.6 12 14.0 Oxyurostylis smithi (C) 2 0.7 0.6 12 14.0 Gammaridae (undet.) (A) 2 0.7 0.6 12 14.0 Hemipholis elongata (0) 2 0.7 0.6 12 14.0 Cu-nd 0.7 0.6 12 Polynoidae et.) (P) 2 14.0 Edotea montosa (P) 1 0.3 0.6 12 20.5 Nucula proxima (M) 1 0.3 0.6 12 20.5 Lyonsi hyalina (P) 1 0.3 0.6 12 20.5 Sabellaria vulgaris (P) 1 0.3 0.6 12 20.5 Oligochaeta Fun-det.) 1 0.3 0.6 12 20.5 Cirratulidae (undet.) (P) 1 0.3 0.6 12 20.5 Table 32.(Cont.) SB18 Rank Total Number/0.05m2 Estimatel by Species Number -x SD Number/m Number ------------------------------------ Collection Date 17 August 1978 ------------------------------------ Lumbrineris tenuis (P) 7 2.3 0.6 42 1.0 Panopeus herbstii (D) 4 1.3 0.6 24 2.5 -Tharyx marioni (P) 4 1.3 1.2 24 2.5 Relita appendiculata (A) 3 1.0 1.7 18 4.0 Cyathura burbanki (1) 2 0.7 0.6 12 6.5 Scoloplos sp. (P) 2 0.7 1.2 12 6.5 Glycinde solitaria (P) 2 0.7 0.6 12 6.5 Paraprionospio pinnata (P) 2 0.7 0.6 12 6.5 'Remertina (undet-.) 1 0.3 0.6 6 13.5 Hemipholis elongata (0) 1 0.3 0.6 6 13.5 Nucula proxima (M) 1 0.3 0.6 6 13.5 §abella-r-iaZ,j@ilaris (P) 1 0.3 0.6 6 13.5 Pista cristata (F) 1 0.3 0.6 6 13.5 Heteromastus filiformis (P) 1 0.3 0.6 6 13.5 Nereis succinea (P) 1 0.3 0.6 6 13.5 -Krabelf-- a tricolor (P) 1 0.3 0.6 6 13.5 Notomastus sp. (P) 1 0.3 0.6 6 13.5 Polynoidae (undet.) (P) 1 0.3 0.6 6 13.5 Table 33. Species diversity, evenness and richness values for Sewee Bay grab samDles from August 1977 to August 1978. First Quarter = samples collected before dredging; Second Quarter = samples collected immediately after dredging; Third Quarter.= samples collected 3 months after dredging; Fourth Quarter samples collected 6 months after dredging and 1 year after first quarter samples. Diversity (H') Evenness (J') Richness (SR) First Second Third Fourth First Second Third Four@h First Second Third Tourth Station Quarter Quarter Quarter Quarter Quarter Quarter Quarter Quarter Quarter Quarter Quarter Quarter Station SBOl 2.06 2.02 3.61 1.63 0.65 0.72 0.76 0.58 1.91 1.73 5.99 1.76 SBOl SB02 1.95 2.73 0.18 3.03 0.69 0.86 0.11 0.96 1.63 2.35 0.44 2.89 SB02 SB03 0.44 3.66 3.85 3.48 0.28 0.94 0.85 0.94 0.60 4.25 4.99 3.80 SB03 SB04 3.24 2.7.3 3.03 1.97 0.90 0.74 0.80 0.62 3.20 3.35 3.42 1.95 SB04 SB05 2.19 3.29 2.98 2.48 0.63 0.89 0.86 0.96 2.63 3.83 2.79 2.09 SB05 SB06 2.35 3.02 2.23 2.32 M8 0.91 0.70 1.00 2.08 2.83 1.94 2.48 SB06 SB07 3.30 4.29 3.84 3.65 0.89 0.90 0.84 0.86 3.68 6.65 5.45 4.56 SB07 SB08 2.76 3.78 3.08 1.57 0.87 0.91 0.74 0.61 2.55 4.17 3.81 1.28 SB08 SB09 2.45 2.91 2.91 2.07 0.74 0.61 0.75 0.74 1.90 5.24 2.85 1.94 SB09 SB10 2.48 1.81 3.65 2.27 0.67 0.78 0.77 0.63 2.72 1.52 4.94 2.24 SB10 SBll 1.89 2.09 2.70 2.16 0.60 0.61 0.75 0.72 0.47 2.09 2.32 1.48 SBll 1.78 2.31 3.07 2.11 0.69 0.73 0.77 0.70 1.17 1.83 3.46 1.84 SB12 SB13 1.24 2.92 2.38 2.42 0.44 0.84 0.67 0.81 1.50 3.14 2.48 2.23 SB13 SB14 1.88 2.94 3.83 2.09 0.54 0.67 0.78 0.81 2.29 3.91 6.01 1.76 SB14 SB15 1.01 2.78 3.39 1.89 0.30 0.84 0.95 0.63 1.78 2.87 3.81 2.10 SB15 SB16 2.41 2.72 3.73 1.97 0.65 0.70 0.87 0.70 2.82 2.62 4.31 1.42 SB16 SB17 2.34 3.85 3.08 0.92 0.57 0.91 0.81 0.92 3.68 4.68 3.29 0.91 SB17 SB18 1.27 3.86 3.90 3.83 0.38 0.81 0.86 0.92 2.22 5.35 4.83 4.74 SB18 Table 34. Mean abundance and total number of species collected in the Sewee Bay grab samples from August 1977 to August 1978. Mean values indicate number/0.05m2. First Quarter = samples collected before dredging; Second Quarter = samples collected immediately after dredging; Third Quarter = samples collected 3 months after dredging; Fourth Quarter = samples collected 6 months after dredging and 1 year after first quarter samples. FIRST QUARTER SECOND QUARTER THIRD QUARTER FOURTH QUARTER Station 3F Abundance No. Species iF Abundance No. Species -x Abundance No. Species 3F Abundance No. Species SBOl 22.0 9 10.7 7 25.7 27 10.0 7 SB02 13.3 7 10.0 9 30.0 3 5.3 9 SB03 9.3 3 9.0 15 27.3 23 8.0 13 SB04 10.3 12 12.0 13 15.0 14 20.3 9 SB05 15.0 11 7.7 13 12.0 11 3.7 6 SB06 9.7 8 8.0 10 20.7 9 1.7 5 SB07 17.3 13 16.7 27 22.7 24 17.3 19 SBO8 7.7 9 19.7 18 29.0 18 16.3 6 SB09 38.0 10 47.7 27 45.7 15 7.3 7 SB10 27.3 13 4.7 5 64.3 29 45.7 12 SBll 53.7 9 39.3 11 37.7 12 38.3 8 SB12 23.7 6 26.7 9 25.3 16 15.0 8 SB13 18.0 7 8.0 11 28.0 12 7.7 8 SB14 26.3 11 55.3 21 41.3 30 5.7 6 SB15 52.0 10 7.7 10 6.0 12 9.3 8 SB16 23.3 13 69.7 15 27.3 20 22.7 7 SB17 25.7 17 15.7 19 17.3 14 1.0 2 SB18 19.3 10 51.7 28 31.7 23 12.0 18 53 Table 35. Wet-weight biomass of Sewee Bay grab samples from August 1977 to August 1978. Values represent mean and standard deviation of biomass for all species collected/0.05m2, First Quarter = samples collected before dredging; Second Quarter = samples collected immediately after dredging; Third Quarter = samples collected 3 months after dredging; Fourth Quarter samples collected 6 months after dredging and 1 year after first quarter samples. FIRST SECOND THIRD FOURTH QUARTER QUARTER QUARTER QUARTER Station 3E SD SD _iE SD 3E SD SBOl 0.26 0.17 0.16 0.15 0.86 0.94 0.09 0.06 SB02 0.06 0.02 0.13 0.64 0.72 0.53 0.06 0.08 SB03 0.06 0.08 0.13 0.09 0.16 0.11 0.41 0.16 SB04 0.50 0.55 0.34 0.45 0.22 0.11 0.10 0.03 SB05 0.81 0.56 1.46 2.29 0.11 0.08 0.27 0.39 SB06 0.40 0.55 1.37 1.55 0.18 0.02 0.07 0.11 SB07 0.14 0.13 2.24 3.78 1.78 2.74 0.56 0.31 SB08 0.12 0.14 0.20 0.07 0.16 0.05 0.22 0.16 SB09 0.40 0.35 0.30 0.28 0.19 0.03 0.07 0.06 SB10 0.25 0.22 0.04 0.02 0.33 0.08 1.41 0.91 SBll 0.29 0.72 1.53 2.32 0.70 0.67 0.38 0.21 SB12 0.47 0.23 0.23 0.09 0.98 1.48 0.14 0.09 SB13 5.25 8.82 0.07 0.06 0.20 0.04 0.09 0.11 SB14 2.89 4.96 0.49 0.35 0.27 0.26 0.32 0.55 SB15 7.02 11.59 0.26 0.27 0.09 0.12 0.49 0.16 SB16 0.25 0.29 0.60 0.67 0.34 0.17 1.67 2.17 SB17 2.34 2.63 2.38 3.99 0.35 0.28 0.05 0.04 SB18 0.08 0.06 0.28 0.13 0.74 0.10 0.54 0.50 54 Immill Illm 3 6668 14104 1212