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NIOZ-RAPPORT 1998- 5
THE MACROBENTHIC FAUNA IN THE DUTCH SECTOR
OF THE NORTH SEA IN 1997 AND A COMPARISON WITH
PREVIOUS DATA
S.E. Holtmann, G.C.A. Duineveld, M. Mulder, RA.W.J. de Wilde
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Monitoring Macrozooberithos of the North Sea
THE MACROBENTHIC FAUNA IN THE DUTCH SECTOR OF THE NORTH
SEA IN 1997 AND A COMPARISON WITH PREVIOUS DATA
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S.E. HOLTMANN, G.C.A. DUINEVELD, M. MULDER, P.A.W.J. DE WILDE
This report presents data of the monitoring program of macrozoobenthos in the Dutch
Continental Shelf (DCS) of the North Sea, a cooperation between the National Institute for
Coastal and Marine ManagementfRlKZ (Rijkswaterstaat), the North Sea Directorate
(Rijkswaterstaat) and the Department of Marine Ecology (NIOZ)
NETHERLANDS INSTITUTE FOR SEA RESEARCH
Monitoring Macrozoobenthos of the North Sea
NIOZ-RAPPORT 1998-5
Monitoring macrozoobenthos North Sea 1997
1.
SUMMARY
ifi continuation of the benthic monitoring project carried out in the period 1991-1996, a
survey of the macrobenthos in the Dutch Continental Shelf (DCS) was made in spring
1997. The survey forms a part of the ‘Biological monitoring programme of marine waters’
(BIOMON, EXP*BMN) commissioned by the National Institute for Coastal and Marine
Management (RIKZ). The purpose of the project is to obtain insight into the year-to-year
variations of the macrobenthic assemblages and to detect trend-like changes, that possibly
indicate anthropogenic influences on the marine environment (e.g. eutrophication,
pollution, beam-trawl fishery).
The present report describes the results of the survey in 1997 and compares these
results with data obtained during previous BIOMON surveys in 1991-1996, the ICES
North Sea Benthos Survey (ICES-NSBS) in 1986 and the MILZON-BENTHOS
programme (1988-1993). Using the existing knowledge about the spatial distribution of
the macrobenthic fauna of the North Sea (Holtmann et al., 1996b), the DCS was divided
into four subareas, i.e. the southern part of the Dogger Bank (DOG), the Oyster Ground
(OYS), the Coastal area (COA) and the more Offshore area (OFF).
In the period between 3 March and 18 April 1997 boxcore samples were taken at
400 selected stations spread over the DCS for study of the benthic fauna and various
abiotic parameters. The abiotic parameters are considered to characterize the relevant
environmental conditions at the time of sampling and in combination with earlier data
give an idea about the temporal variation of the environment. The median grain size of
the sediment showed an increase in the first part of the monitoring project, in the period
between 1986 and 1995. This trend was not continued until 1997, but changed into a
decrease from 1995 to 1997. The content of mud (particles 16-63 jam) seems to decrease
between 1990/1992 and 1997 in the whole study area.
The benthos samples collected in spring 1997 yielded a total number of 231
species/taxa. As in previous years, polychactes are the most dominant taxon in the DCS,
representing 45 % of the total number of species. The highest values for species richness
(Hill0) and Shannon-Wiener index were found in 1997 in the northern part of the DCS
(Dogger Bank and Oyster Ground), which also had the lowest values for Simpson
dominance index. In comparison to the previous year, biodiversity of the macrobenthos
was higher in 1997. Total density and biomass in 1997, however, were in the same range
as in 1996, though in the Oyster Ground the total biomass seems to decrease between
1994 and 1997. In the whole study area the observed trends among individual species
were in most of the cases changes in downward direction. The results of a DECORANA
ordination with the combined data show that the species composition of the 1986 and
1990 samples deviates from later years in all subareas. In the Coastal and Offshore area a
difference was found between the species composition in 1997 and previous years.
1
Monitoring macrozoobenthos North Sea 1997
2. SAMENvATTING
g
0
Als vervoig op het benthos monitoring project in de penode van 1991 tot 1996 is er in het
voorjaar van 1997 de volgende bemonstering van het macrobenthos op het Nederlands
Continentale Plat (NCP) uitgevoerd. Het onderzoek maakt deel uit van het ‘Biologisch
Monitoring programma zoute wateren’ (BIOMON, EXP*BMN) in opdracht van het
Rijksinstituut voor Kust en Zee (RIKZ). Met het project wordt beoogd inzicht te krijgen
in de jaarlijkse fluctuaties van de macrobenthos gemeenschappen en vast te stellen of er
op de langere termijn trendmatige veranderingen optreden. Dergelijke veranderingen
zouden onder meer kunnen plaats vinden als gevoig van effecten van anthropogene
activiteiten (bijv. eutrofiering, verontreinigin~, boomkorvisserij).
In het voorliggende rapport zijn de resultaten van de bemonstering in 1997 samen
gevat en vergeleken met aanvullende informatie uitgewerkt in het kader van het
BIOMON project 1991-1996, het ICES Noordzee Benthos onderzoek (ICES-NSBS) in
1986 en het MILZON-BENTHOS programma (1988-1993). Op basis van de aanwezige
kennis over de ruimtelijke verspreiding van het macrobenthos op de Noordzee (Holtmaxm
et al., 1996b) is het NCP ingedeeld in vier deelgebieden, te weten het zuidelijke deel van
de Doggersbank (DOG), de Oestergronden (01’S), de kustzone (COA) en het Offshore
gebied (OFF).
In de periode van 3 maart tot 18 april 1997 zijn er in het hele onderzoeksgebied op
100 geselecteerde stations boxcore monsters genomen om een aantal abiotische en
biotische factoren van het NCP te bestuderen. De abiotische factoren illusteren de milieu
omstandigheden tijdens de bemonstering en geven een beeld over de tijdelijke fluctuatie
van de omgevingsfactoren. De mediane korreigrootte van het sediment laat een toename
zien in het eerste gedeelte van het monitoring tussen 1986 en 1995. Deze trend heeft zich
niet doorgezet tot 1997 maar is veranderd in een afliame van 1995 tot 1997. In het hele
onderzoeksgebied lijkt het sub gehalte (partikels 16-63 [im) afte nemen in de periode van
1990/1992 tot 1997.
Het sorteren van de benthos monsters in 1997 resulteert in een totale aantal van 231
soortenltaxa. Evenals in voorafgaande jaren zijn de polychaeten in 1997 het meest
dominante taxon van het NCP en representeren 45 % van de totale aantal soorten. De
hoogste waardes van het soorten rijkdom (Hill0) and van de Shannon-Wiencr index werd
in 1997 in het noorden gevonden (Doggersbank en Oestergronden), terwiji in dit gebied
ook de laagste Simpson dominantie index is gemeten. De biodiversiteit van het
macrobenthos in 1997 was hoger dan in het onderzoeksjaar van 1996. De totale dichtheid
en biomassa waren in 1997 in de zelfde orde van grote dan in 1996. In de Oestergronden
is in de periode van 1994 tot 1997 een afhame van de totale biomassa geconstateerd. In
het hele onderzoeksgebied laten de trends op soort-niveau in de meeste gevallen een
athame zien. Op basis van de DECORANA ordinatie techniek zijn er verschillen
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Monitoring macrozoobenthos North Sea 1997
gevonden in soorten samenstelling voor de jaren 1986 en 1990 in het hele
onderzoeksgebied en voor 1997 in de kustzone en in het Offshore gebied.
3. INTRODUCTION
In 1989 the BIOlogical MONitoring programme of marine waters (BIOMON, EXP*
BMN) was started with the goal to study the temporal variation of the marine ecosystems
in the Dutch Continental Shelf (DCS) including the Wadden Sea and the Delta area. It is
an initiative, of the National Institute for Coastal and Marine Management of
Rijkswaterstaat (RIKZ) in association with several Dutch institutes (Yland, 1995). The
subject of this long-term monitoring programme comprises besides the macrobenthos also
plankton, fish, seagrass, hard substrate populations, seabirds and mammals.
The present report gives an overview of the results of the macrozoobenthos survey
carried out in spring 1997. The objective of this series of surveys is to study year-to-year
variations and to detect possible trend-like changes in the macrozoobenthos communities
living in the Dutch DCS of the North Sea. The results of previous surveys from the period
1991-1996 have been published by Duineveld (1992), Duineveld & Belgers (1993; 1994)
‘andHoltmannetal. (1995; t996a; 1997).
The spring 1997 survey is the third study since 1995 to which the new sampling
strategy for the monitoring programme of macrozoobenthos (see Essink, 1995) is applied.
In this new strategy, based on a stratified random sampling design, only one sample per
station is taken at a large number of stations. It represents a break with the earlier strategy
in which more replicate samples were taken at a smaller number of stations. The reason
for the switch is that with the new method a statistically more accurate insight can be
acquired in the benthic communities in the whole of the DCS (van der Meer, 1997).
Moreover, the aim of the BIOMON programme is to detect trend-like changes in the
macrobenthic communities in the major parts (habitats) of the whole DCS rather than at
single stations.
The combined results from the surveys in the period between 1991 and 1996
include numerous fluctuations in species densities as well as in values for community
variables (e.g. biodiversity). Nevertheless, no consistent trends could be detected in the
total macrobenthos density or biomass nor in the abundances of most of. the selected
macrobenthic species (Holtmann et al., 1997). The data on the general sediment
characteristics suggest a slight decrease of fine material between 1986 and 1996 on the
Dutch Continental Shelf However, changes in analytical methods may partly explain
these differences in sediment composition (Zonneveld, 1994).
3
Monitoring macrozoobenthos North Sea 1997
4.
wa~
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MATERIAL AND METHODS
4.1.
SAMPLING METHODS
The sampling grid (Fig. 1) forms the basis for an annual survey of a monitoring project
which take place in spring to early summer. In order to optimize the information output
with the lowest possible effort, a new sampling strategy was adopted in 1995. During
earlier BIOMON surveys (1991-1994), 5 replicate boxeore samples were collected from
25 locations. These stations were located on 4 transects perpendicular and 1 transect
parallel to the Dutch coastline (Duineveld, 1992). With the new strategy a total of 100
stations are sampled and only one sample is taken per station. Prior to the sample site
selection for the new strategy, the study area was divided into 4 subareas, viz, the
southern part of the Dogger Bank (DOG 7 stations), the Oyster Ground (OYS 42
stations), the Coastal zone (COA 15 stations) and the Offshore (OFF= 36 stations) area.
The number of stations per subarea depends on its extent. The 100 stations that were
selected include the 25 old BIOMON stations and 75 additional stations which are more
or less randomly distributed over the DCS (Essink, 1995). To ensure that any changes
that are observed are not due to methodological differences, the procedures for sampling
and processing the samples are standardized (Essink, 1991) and have remained unaltered
since the beginning of the project in 1991.
The 100 selected stations were sampled in the period 3 March to 18 April 1997. The
northern and eastern part of the DCS (40 stations) was visited with the RV. Pelagia
(NIOZ). The more southern and Coastal stations were sampled with the RV. Holland
(North Sea Directorate RWS). Two Coastal stations with a water depth less than 10 m,
viz. COA 13 & 14, were visited on 18 April 1997 with the RV. Argus (RWS). In Fig. 1 an
overview of the sampling stations in spring 1997 is given. Table l(a/b) summarizes the
geographical positions of the 100 stations, together with the former station codes and
selected abiotic characteristics (depth/sediment) of the stations. More general information
about the cruise carried out with the RV. Holland and the weather conditions during this
part of the survey in 1997 can be found in the cruise report of Rijkswaterstaat
(Anonymous, 1997).
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4.2.
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SAMPLE TREATMENTS
At each station shown in Fig. 1 two boxcore samples (0.068 m2, minimal depth 15 cm)
were taken while the ship was anchored. One of the samples was used for sediment
analysis and the other sample was washed through a sieve with round holes (1 mm) to
collect the macrobenthic fauna. For sediment analysis 2 pooled subsamples (3.4 cm Ø~
depth 10 cm) were immediately stored at -20°C. The residue of the macrobenthos samples
4
1977
three
diver
Monitoring macrozoobenthos North Sea 1997
was preserved in a borax-buffered solution of 4-6 % formaldehyde in seawater and stored
at room temperature.
In the laboratory the macrobenthos samples were stained with rose-bengal and
washed over a set of nested sieves with 0.7 mm as the smallest mesh size to facilitate
sorting. The macrofauna was identified to species level, except for some notoriously
difficult taxa such as anthozoans, hydrozoans, phoronids, priapulids and nemerteans, and
subsequently counted. Sizes (nearest 0.5 mm) were recorded for most molluscs and
echinoderms.
4.3. As~rn~ DRY WEIGHT
The ash-free dry weight (AFDW) of the different taxa was determined in one of the
following ways:
1.
•
•
Molluscs and echinoids: by means of length-AFDW relationships of the form
W=a*L’~ (W=AFDW in g and L4ength in mm)
Folychaetes. other worms, lareer crustaceans and ophiuroids: indirectly, by
converting the (blotted) wet weight into AFDW by means of conversion factors!
provided by Rumohr et al. (1987) and Ricciardi & Bourget (1998). Wet weights were~
measured with a Mettler P1300 balance to the nearest mg.
Remaininz taxa: directly, by drying a sample at 60 °C for at least 60 hours and
subsequently incinerating at 520°C for 2 hours (Duineveld & Wine, 1987).
Small molluscs, amphipods and cumaceans were assigned an average individual AFDW
of 0.2-0.5 mg. The same figure is used by Holtmann & Groenewold (1992; 1994) in their
analysis of macrobenthos from the MILZON-BENTHOS project in the southern North
Sea between 1991 and 1993. This estimated individual weight is based on previous
determinations of the AFDW of the taxa in question (Duineveld; Holtmann, unpubi.).
4.4. S’r~’ns’ncs
In addition to the density (ind./m2) and biomass (g AFDW/m2) the diversity of each
macrobenthos sample was calculated. In recent literature a suit of biodiversity indices
have been used to identif~’ possible changes of the benthic fauna (Hill, 1973; Peterson,
1977; Pearson & Rosenberg, 1978; Harper & Hawksworth, 1994). In this report, we used
three indices each representing a different aspect of the distribution of the sample
diversity. The species richness (Hill0) stands for the number of species per boxcore
5
Monitoring macrozoobenthos North Sea 1997
imple and is the simplest index. The other two indices, the Shannon-Wiener index (H’)
;hannon & Weaver, 1949) and the Simpson index (D) for dominance (Simpson, 1949),
t based on the proportional abundances of the individual species in the samples. The
impson index is sensitive to the abundance only of the more plentiful species and can
ierefore be regarded as a measure of dominance (Hill, 1973). A high Simpson index
Leans low diversity, whereas a high value for the Hill0 or Shannon-Wiener index
idicates high diversity.
In order to highlight the trends in certain variables over time, scatter plots were
noothed with the LOWESS method (Cleveland, 1979; 1981). This produces a smooth
arve by running along the X values and finding predicted values from weighted averages
f nearby Y values (see for details Wilkinson, 1990). The total density and the densities
f the macrobenthos taxa were scaled by a log (x+1) transformation to reduce the
ifluence of outliers (clumped distribution),
To illustrate the differences between the 4 subareas of the DCS and the significance
f differences, notched Box-Whisker plots were drawn. The notches surrounding the
iedians provide a measure of the rough significance of differences between the median
alues. If the notches around two medians do not overlap, the medians are roughly
[gnificantly different at the 95 % confidence level (McGill et cii., 1978). All the scatternd Box-Whisker plots were made with the program SYSTAT (version 5.0) (SYSTAT
~c. IL, USA).
Box- Whisker plot:
o—far outside value
* —outside value
~ upper extreme
upper hinge
—median nbtches
—lower hinge
—
lower extreme
6
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Monitoring macrozoobenthos North Sea 1997
Possible changes in the species assemblages in the 4 subareas during the period 19861997 were resolved with the ordination technique DECORANA (DEtrended
CORrespondence ANAlysis). For that reason the FORTRAN program CANOCO
(version 2.2) was used (Hill, 1979; Hill & Gauch, 1980; Ter Braak, 1986). The input data,
i.e. average species abundances per subarea of each research year, were sealed by a linear
transformation.
4.5.
SEDIMENT ANALYSIS
At each station shown in Fig. 1, two subsamples were taken from an intact boxcore
sample and subsequently pooled for laboratory analysis of the sediment composition (e.g.
grain size, content of calcium carbonate). The grain size was analysed with a Malvem
Particle Sizer (MPS) by the laboratory of the National Institute for Coastal and Marine
Management (RIKZ, Middelburg). Two parameters were derived from the grain size data:
the percentage (by weight) of mud (particles 16-63 jam) and the median grain size (jam).
The latter value was calculated using the entire size range (thus including the mud
fraction).
Sediment types were classified on the basis of the median grain size as follows:
Characterisation of the sedimenttype according to
the median grain size (after Gullentops et al., 1977).
<175 jam
Very fine sand
175-250 p.m
Fine sand
250 300 p.m
Fine-medium sand
300 350 jam
Medium-coarse sand
>350 jam
Coarse sand
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7
I
Monitoring macrozoobenthos North Sea 1997
5. RESULTS
5.1. CHANGES IN SEDIMENT COMPOSITION
Except for one Oyster Ground station (OYS 37) sediment data are available for the whole
DCS in 1997. The median grain size, as well as the mud content of the samples are given
in Table 1(alb). This table summarizes also the water depth and the sampling date. The
spatial distribution of median grain size, mud content and depth recordings (not corrected
for differences due to the tidal cycle) in spring 1997 are depicted in Figs. 2-4.
Table 2 shows the mean values of sediment parameters for the 4 distinguished
subareas in 1997. Comparing the values withthe data of 1996 (Holtmann et al., 1997), it
appears that they have similar ranges but the averages in 1997 were somewhat lower. The
southern Dogger Bank and the shallow Coastal stations have sediments consisting of fine
sand with a low mud content (in 1997 mean: 0.t-O.5 %). The deeper Oyster Ground area
are characterized by very fine sand with high mud content (in 1997 mean: 5.8 %, max. 25
% at UI’S]]). The Offshore area had the highest average value for median grain size but
with a relatively large variation compared to the other subareas (mm. 184 jam at OFF 3,
max. 499 jam at OFF 29; Table 2).
Figs. 5 & 6 illustrate the year-to-year variation in the sediment composition in the
period between 1986 and 1997. These two figures based on the same number of
observations, whereas in Fig. 6 in areas where the mud content was found to be zero in
several samples only one symbol is given. The increasing trend of the median grain size
as found in 1995 was not continued till 1997 (Fig. 5). On the contrary, a slight decrease of
the median grain size can be observed on the southern Dogger Bank and the Coastal
stations between 1995 and 1997. It should be stressed that the sieving method used for
sediment analysis in the 1980’s was replaced by the Malvern Particle Sizer (MPS) which
complicates the comparison between these early data and those from the 90’s (see
Zonneveld, 1994).
The temporal variation of the mud content is given in Fig. 6. The mud content
seems to decrease between 1990/1992 and 1997 in the whole DCS. The high percentages
of the mud found during the 1992 survey were not found again in the period 1993-1997.
In the Offshore and Coastal area, the percentage of mud (particles 16-63 jam) was zero in
1997, except for the 8 % mud content at the Coastal station COA 5 (Table 1). Also at the
Dogger Bank very low percentages of mud were found between 1994 and 1997. The mud
content in the Oyster Ground showed a higher deviation in 1997 than in 1996, but with a
lower mean value in the last year of monitoring (Fig. 6; Table 2).
8
Monitoring macrozoobenthos North Sea 1997
5.2. DIsTRIBuTION OF THE MACROBENTHIC FAUNA IN 1997
5.2.1. DIvERsITY
In 1997 a total number of 231 species/taxa were identified in the 100 bottom samples. Of
these, 23 species are juvenile and identified to genus level only. The distribution of the
species over the stations (presence/absence) and the scientific names are given in
Appendix-i. The basic data of macrobenthic abundance, biomass and diversity are
summarized in Appendix-2. In Table 2 the mean values of the major parameters found in
the 4 subareas in spring 1997 are given.
The most species-rich group in 1997 were the Polychaeta, to which 45 % of the
species found in the DCS belong. Approximately 23 and 20 % of the identified species
belong to the Crustacea and Mollusca respectively and only 6 % to the Echinodermata of
which 14 species were found. The remaining 6 % of the species are recorded as
miscellaneous at higher taxonomic level. The most common species, i.e. ones that were
found at more than 15 % of the sampling stations, are listed in Table 3. As expected, the
main part of these species are polychaetes. The species with the highest mean densities in
the whole DCS are the polychaetc Magelona papillicornis and the echinoderm Amphiura
fl4formis (viz. 153.3 and 104.5 ind./m2). In the whole DCS the highest mean biomass was
measured for Echinocardium cordatum and Spisula subtruncata (viz. 3.23 and 1.17 g
AFDW/m2) (Table 3).
The spatial variation in species richness or Hill0 is mapped in Fig. 7. Values for
Hill0 varied between 3 and 46 species per boxcore sample (viz. COA 3 & QYS 20). In
general the diversity was somewhat higher in 1997 than was measured in 1996 (Table 2).
The species richness shows a clear gradient in north/south direction (Fig. 7). The stations
in the southern part of the Dogger Bank (mean: 35.4 species) and the Oyster Ground
(mean: 29.1 species) yielded on average the highest species number per sample, whereas
on the southern locations a lower species richness was found (Table 2). Another measure
of biodiversity, the Shannon-Wiener index, was also highest in the northern subareas. The
high values of the Simpson dominance index along the Dutch coastline indicate a low
diversity. In this area, the values for the Hill0 and Shannon-Wiener indices were in 1997
much lower than in the rest of the DCS.
5.2.2. DENsITY AND BIOMAS5
The mean density (ind./m2) and biomass (g AFDW/m2) in the 4 subareas are summarized
in Table 2. The spatial variation of total density and biomass are shown in Figs. 8 & 9. In
all subareas the total density of 1997 was in the same range as in previous years. The
Dogger Bank had the highest average density of all subareas and the Offshore stations the
lowest. The highest density (4681 ind./m2) was found at the Oyster Ground station OYS
9
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Monitoring macrozoobenthos North Sea 1997
md the lowest (102 ind./m2) at the Coastal station (COA 13). The distribution of the
thers over the taxa follows the same pattern as the total number of species, viz, in all
areas polychaetes are the numerically dominants taxon, followed by the crustaceans
molluscs (Table 2). In the Oyster Ground, echinoderms constitute an important share
he macrofauna depending on the abundances of the ophiuroid Amphiura Ji4formis.
Mean total biomass and biomass of 4 major groups in the four subareas is shown in
le 2. Except for the Offshore area, in 1997 the total biomass was found to be generally
iewhat lower compared with 1996. The range of biomass figures varied from 0.04 g
)A 13) to 115.29 g AFDW/m2 (COA 9) (Table 2). Of the four subareas, the Dogger
ik had on average the lowest total biomass. Along the Dutch coast the group of
[luscs reached the highest biomass due to locally high abundances of bivalves (Ensis
?ctus and Spisula subtruncata). Crustacean biomass was highest in the Oyster Ground
ause of the presence of the burrowing shrimp Callianassa subterranea. ft the
thore area, the heart urchin Echinocardium cordatum is responsible for the high
mass of echinoderms. The highest average biomass of the polychaetes was found in
Oyster Ground due to the dominance of tube worm Chaetopterus viiriopedatus.
TEMPoRAL VARIATION OF THE MACROBENTIIIC FAUNA
Dogger]
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.1. VARIATION IN THE ABUNDANCE OF INDIVIDUAL SPECIES
The decn
The densi
~s. 10-13 depict the temporal variation in density of selected species in the 4 subareas
ing the period 1986 and 1997. The selected species are ones that are widely distributed
I occur on more than 15 % of the locations (Table 3). The selection is the same as in
previous report on the 1996 survey (Holtmann et al., 1997).
downwan
gger Bank (Fig. lOaJb)
r the southern part of the Dogger Bank only a few data are available from the period
90-1994 as only one station was visited in those years. Most species in Fig. 10 show an
rease in abundance in the beginning of the survey period but this changed into a
wnward trend in 1993/1994 (Holtmann et al., 1997). Inmost species this decrease was
I continued in 1997 though abundances were still quite low in the species Bathyporeia
gans and Lanice conchilega (Fig. lOa). As in the two previous years, the polychaete
~ge1ona papillicornis was found to be a dominant species on the Dogger Bank in 1997
can: 284 ind./m2).
‘ster Ground (Fig. 1 la/b)
tause of the relatively large number of observations in the Oyster Ground between
86 and 1997, the density fluctuations of the species are better covered than on the
10
5.3.2. VA
The temi
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Diversity’
The spati2
1997. Dur
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1997. TM.
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Shannon-i
Monitoring macrozoobenthos North Sea 1997
Dogger Bank. A remarkable finding is the downward trend of the burrowing crustacean
Callianassa subterranea (mean density in 1997: 23.3 indJm2). Together with the species
Amphiura fll4formis and Mysella bidentata, Callianassa can be regarded as a
characteristic species of the Oyster Ground. Also densities of the two other characteristic
species A. fi4formis and M bidentata continued to decrease in 1997.
Offshore (Fig. l2aJb)
In the Offshore area most of the selected species showed no consistent trend between
1986 and 1997. The mean density of for example the polychaete Neph/ys cirrosa is quite
stable during the last 3 years of monitoring (mean density in 1997: 52 ind./m2). The
exceptional high values of the density of Echinocardiuin cordatum as observed in 1989
was not found again in the period 1990 to 1997. Among the densities of the amphipod
Bathyporeia elegans a maximum of 1829 ind./m2 was found in 1997, a value which was
not found earlier (mean density in 1997: 188 ind./m2).
Coast (Fig. 13a-c)
in most of the species a downward trend was noticed along the Dutch coast in the period
1986-1997. Low densities of the molluscs Natica alden and Tellina fabula were already
observed in spring 1996. In 1997 the mean density ofT fabula was found to be 6 ind./m2
while N. alden was not found anymore in the Coastal zone in the last year of monitoring.
The decrease of Echinocandiuni cordatum as observed in 1996 was continued in 1997.
The density of the polychaete Nephtys hombengii showed in the Coastal area also a clear
downward trend between 1986 and 1997.
5.3.2. VARIATIoN IN DIVERSITY, DENSITY AND BIOMASS
The temporal variation of biodiversity, total density and biomass of the whole
macrobenthic fauna as well as of the 4 major taxa (viz. polychaetes, crustaceans, molluscs
and echinoderms) are illustrated in Figs. 14-20.
Diversity (Figs. 14-16):
The spatial pattern of diversity in the DCS as found in previous years had not changed in
1997. During the whole monitoring period the highest diversity was found on the Dogger
Bank and the Oyster Ground. The 1997 values for Hill0, i.e. the number of species per
sample or species richness, in the four subareas were in general higher than measured in
1996 (Table 2). Hence, the decrease in diversity as found in 1996 was not continued in
1997. This was clearly noticeable on the Dogger Bank where in 1997 on average 35.4
species per sample were found (1996: 28.7). Tn the Coastal area the extremely low Hill0
diversity of 8.0 species per samples in 1996 changed to 12.4 in 1997 (Fig. 14). The
Shannon-Wiener diversity showed a similar development as Hill0, i.e. the increased
11
P.
Monitoring macrozoobenthos North Sea 1997
Lues in 1997 may mark the end of a downward trend of this index over the period 198696 (Fig. 15). Simpson index, expressing the degree of dominance by the few most
indant species, was quite low in 1997. On the southern part of the Dogger Bank,
npson index showed the lowest fluctuation. In this area a slight decrease was found in
last 3 years of monitoring. In the Oyster Ground, the high values of Simpson index in
93 were followed by a decrease until the survey of 1997 (Fig. 16).
~nsitv (Figs. 17/18a-d):
ioverview of the total macrobenthic density in 1997 is given in Table 2. In 1997 the
al density in the subareas was in the same range or somewhat higher than in 1996. The
~hest total density in the 4 subareas was measured in the period 1994/1995. On the
uthem part of the Dogger Bank, the initial increase of the total density changed into
crease in 1994 (Fig. 17). This trend coincided with the trends in crustacean and mollusc
nsity, both of which slightly decreased during the period 1994-1997 (Fig. 18a).
The total abundance in the Oyster Ground showed little variation during the years
monitoring. The highest mean values were found in the period between 1992/1994.
ie 4 major taxa showed in general the same pattern. However, the density of the
hinoderms was quite low in 1995 due to low densities of the otherwise common
hiuroid AmphiuraJIflformis (Fig. 18b).
In the Coastal and the Offshore areas more variation and extreme values were
und. The density of all major groups in the Offshore area showed a downward trend
tring the last 3 years, except for the crustaceans which were quite stable over the years
ig. 18c). The total density along the Dutch coast was much lower in 1996 and 1997
an found in the period between 1986 and 1995. The most distinct decrease was
served among the crustaceans and molluscs (Fig. 1 8d), which can be partly explained
i relatively low densities of the bivalves Tellina fabula and Spisula subtruncata (Fig.
~omass (Figs. 19/20a-d):
~ie temporal variation of the total biomass in the 4 subareas is shown in Fig. 19. Total
omass on the Dogger Bank tended to increase in the period between 1986 and 1996 but
Le rather low mean of 5.5 g AFDW/m2 in 1997 represents a break in this trend (Table 2).
1996 a mean biomass of 14.5 g AFDW/m2 was found in the southern part of the
ogger Bank due to the high biomass of molluscs (Holtmann et aL, 1997). Though on the
ogger Bank in 3 of the macrobenthos groups an upward trend was found in the first
ears of monitoring, no trend was observed in this area in the last investigation years
?ig. 20a).
In the Oyster Ground, a decrease of the total biomass was noticed in the last 3 years
[994 to 1997; Fig. 19). The mean total biomass in 1997 was found to be 12.8 g
~FDW/m2 while in 1994 this figure was nearly 20 g AFDW/m2 (Fig. 19). This decline
12
cones1
crustac
little v~
and 19
Only 1]
since 1
which:
trends 1
5.3.3.
The DI
assemb
subarea
from tF
subarea
to years
Fi
of the
separate
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the muc
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there w
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TI
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1997). Ii
monitori
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part of tI
Monitoring macrozoobenthos North Sea 1997
corresponded with the trend in biomass of echinoderms and to some extent also of
crustaceans. The biomass of polychaetes and molluscs in the Oyster Ground showed only
little variation during the monitoring period (Fig. 20b).
The total biomass in the Offshore and Coastal areas were quite stable between 1986
and 1997 (Fig. 19). The same is true for the biomass of the 4 major groups (Fig. 20c/d).
Only the crustacean biomass in the Coastal area showed a continuous downward trend
since 1988, but it forms only a minor part of the total biomass. The biomass of molluscs
which forms the major part of the total biomass along the coast does not show any clear
trends between 1986 and 1997 (Fig. 20d).
5.3.3. COMPARISON OF SPECIES ASSEMBLAGES
The DECORANA ordination technique was used to reveal possible changes in species
assemblages of the Dutch part of the North Sea. One ordination (Fig. 21) was made of all
subareas together using the yearly average abundances of 400 species/taxa in the areas
from the period 1986-1997. Furthermore, an ordination was made for each of the 4
subareas separately (Fig. 22). In these figures the points that are close together correspond
to years that are more similar in species composition, than points that are more separated.
Fig. 21 shows the two major ordination axes and the corresponding yearly positions
of the subareas. The 4 subareas of the Dutch part of the North Sea remain clearly
separated throughout the whole period of monitoring which indicates that there exists a
fundamental difference in species composition. Because of the wide separation between
the muddy Oyster Ground and the sandy Offshore area, sediment characteristics seem to
be one of the most plausible explanations for the differences in Fig. 21 (see Table 2). The
relatively compact clusters of points belonging to different subareas (Fig. 21) suggest that
there were no drastic changes of the species composition in any of the subareas during the
period of monitoring. Only the first years of monitoring (1986, 1990) in the Offshore area
appear to have yielded a somewhat different assemblage than found in later years as
shown by the distance of the points referring to these two periods.
The ordination plots of the 4 subareas are given in Fig. 22. Quite obvious in all 4
plots is a separation between the years 1986-1990 and later years (cf. Holtmann et al.,
1997). In the plots of the Coastal and Offshore area, the point belonging to the last year of
monitoring (1997) is clearly separated from the previous years. This separation which can
indicate changes in species composition was not found in the northern areas, the southern
part of the Dogger Bank and in the Oyster Ground.
Monitoring macrozoobenthos North Sea 1997
IISCUSSION AND CONCLUSIONS
e past decade the macrobenthic fauna has been widely used in ecological monitonng
rammes which studied effects of anthropogenic influences on the marine
ronment (Pearson & Rosenberg, 1978; Govaere et at., 1980; Rees & Eleftheriou,
); Gray et at., 1990; Daan & Mulder, 1996; Bergman et at., 1990). One reason for this
uent use is that soft-sediment infaunal assemblages are comparatively easy to sample
quantitative manner because of their relative immobility. Plankton or fish populations
mobile and may show migratory behaviour. This would enable them to avoid or
pe contaminated areas. By contrast, infaunal macrobenthos is for the major part of
life intimately associated with the sea-bed and hence integrates effects of human
,ities (e.g. offshore mining, pollutants, fishery etc.) over a long time. Despite their
.ive immobility as adults, the pelagic larval stage that most macrobenthic species
;ess allows them to (re)colonise empty habitats.
The extensive investigations of the BIOMON programme have resulted in a large
y of data on the distribution of macrobenthos in the DCS between 1991 and 1997. The
ous presentations of these data in the present report show clear year-to-year variation
lensities of species as well as in attributes of whole assemblages (diversity, total
sity and biomass). Trends are highlighted on the species-level but also among
~mblage attributes to get an impression about the condition of the benthic ecosystem.
ed on the results of the survey of the BIOMON project in 1997 together with
irmation from earlier surveys (ICES 1986, MILZON-BENTHOS 1988-1993,
P*BMN 199 1-1996) the following major observations were made:
The increase of the median grain size observed in the beginning of the monitoring
period (1986-1995) changed into a (slight) decrease between 1995 and 1997.
A decreasing trend was found of the mud content (16-63 gm) between 1990 1992 and
1997 in the whole study area.
The diversity (species richness) of the 1997 samples was in general higher than of
those taken in 1996. Diversity showed a clear north/south gradient: samples from the
northern subareas were more diverse than those from the Coastal and the Offshore
subareas.
In 1997 the total macrobenthic density was in the same range as found in previous
years. Overlooking the whole monitoring period, the highest values for total density
were measured in the period 1994 1995 in all four subareas.
Total biomass was in 1997 somewhat lower than in 1996. Between 1994 and 1997 a
decrease of the total biomass is noticeable in the north of the DCS (Oyster Ground
subarea).
On the species-level, a continuous downward trend was found of Bathyporeia eiegans
(Dogger Bank), Amphiura fii(formis and Calilanassa subterranea (both Oyster
Ground) between 1991 and 1997.
•
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Monitoring macrozoobenthos North Sea 1997
•
•
The period 1991-1997 also showed a clear decrease of Echinocardiurn cordatum,
Nephtys hombergii and Tellina fabula in the Coastal subarea. The gastropod Natica
alden was quite abundant along the coast in the first period of monitoring but absent
from this subarea in 1997. N. alden seems to become more common in the northern
part of the DCS between 1991 and 1997.
In the DECORANA ordination plot of the combined data (1986-1997), the points
marking the 1986 and 1990 observations in the 4 subareas are separated from the
points belonging to later years. This may indicate changes in species composition. For
the Coastal and Offshore subareas also the last year of monitoring (1997) showed a
clear separation.
In spite of all the temporal fluctuation the macrobenthic distribution in the Dutch part of
the North Sea shows quite consistent spatial patterns over the years. This is due to the
relatively stable external circumstances, such as the sediment conditions and the nutrient
supply. The distribution of the various benthic assemblages in the DCS appears to be
strongly correlated with the sediment composition (Table 2). One of the causes for this
relation is that the particle size (and porosity) enables or disables species to live, ingest or
to make permanent burrows. Furthermore, the grainsize of recent sediments reflects a set
of conditions (e.g. current speed, depth, distance from coast) which can be decisive for
the distribution of a species and the maintenance of its population. Muddy sediments are
typically located in deeper quiescent areas where fine particles are not eroded. Such
conditions are also favourable for deposition of nutritious particles. At the muddy Frisian
Front, for example, high amounts of chlorophyll-a are found in the sediment indicating
high concentrations of fresh algal carbon. The sediment composition influences not only
the food availability but also the settlement of the benthic species. Moreover, the
interactions between the benthic organisms (e.g. predation, food competition,
commensalism) can influence the stability of the species distribution in the North Sea.
Species that live in burrows deeper in the sediment are least affected by predation but also
less influenced by man’s uses of the sea (e.g. bottom fishery).
The biodiversity of benthic assemblages has been widely used to indicate the
assemblage stability and to detect changes of the ecosystem (Heip eta!., 1992; Mackie et
a!., 1995). Consistently low diversity of macrobenthos is found in the Coastal and in the
Offshore subareas. In these dynamic habitats only a part of the species present in the
southern North Sea is able to settle and survive. Because of the relatively low species
density in these subareas, 12 to 16 per sample, changes in a few common species has a
greater effect on the assemblage than in the Oyster Ground where normally 35 species are
found in a sample (Table 2). The distinct changes in the Coastal and Offshore
assemblages as illustrated by the DECORANA ordination (Fig. 22) is due to decreases of
some characteristic species viz. Echinocardiurn cordatum, Nephtys horn bergii, Tellina
fabula and Natica alden. The results of following monitoring surveys will show if there
Monitoring macrozoobenthos North Sea 1997
•ontinuation of these changes in species composition in the Coastal and Offshore
7. Acie,u
Next to diversity, individual ‘key’ species’ and their life history provide clues
the conditions within a benthic ecosystem. Highly dynamic or disturbed systems,
can be found along the Dutch coast and in the Offshore area, are inhabited by soopportunistic species having high grow rates and a large reproductive output
;on & Rosenberg, 1978; Arntz & Rumohr, 1986). These characteristics enable them
)idly adapt to environmental perturbation and quickly re-colonise empty habitats
sle & Grassle, 1974; Kirkegaard, 1978; Gray, 1982). This stage of colonisation is
~terised by high abundance’s of only a few species. Hence such immature
blages are indicative for a recent disturbance. In parts with more stable
)nmental conditions, like the central North Sea and the Oyster Ground, slow
ng but relatively long-living species become more abundant. Examples are the
e Aretica islandica, the polychaete Chaetopterus variopedatus and the echinoderm
iura fi4/’orinis (Duineveld ci al., 1987; Holtmann, ci a!. 1996b; Witbaard, 1995).
clear changes occur in the abundance of ‘key’ species, it is likely that some
mental condition in the benthic ecosystem has altered. Such a situation calls for a
detailed study using a denser sampling grid than the one of the BIOMON
imme. An example is the noticed decline of the brittle star Amphiurafihiformis. This
‘s is quite common in the Dutch sector of the North Sea where it was found on 32 °c
stations in 1997 (Table 3). All these stations are located north of the 30 m depth
ir, in the Oyster Ground subarea. The abundance of Amphiua shows a slight
ward trend in the Oyster Ground subarea over the period 1986-1997 (Fig. 1 la). The
,est decrease in Arnphiura density was observed at the Frisian Front where it was
rly quite abundant (> 1000 m 2) The causes for this decline are the subject of a
~d study which focuses on two possible causes namely a reduction of the food
ior a failing recruitment. So far it seems as if the food supply was not the reason for
‘w Amphiura abundance and a natural cause (e.g. population senescence) can
ore not be excluded (Brocken, 1998).
This case underlines the difficulties encountered when interpreting results of
rig monitoring programmes like BIOMON. The natural temporal an spatial
ations in populations and assemblages of species are superimposed on trend-like
es. This requires long time series in order to confirm the tentative conclusions and
‘stallise the changes of the macrobenthic assemblages that are a response to
‘pogenic influences.
The mon
Marine 1\
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NTOZ. Th
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Sea
~s that are characteristic of a specific area, often found with high density or and biomass
16
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Monitoring macrozoobenthos North Sea 1997
7. AcKNOWLEDGEMENTS
The monitoring programme is an initiative of the National Institute for Coastal and
Marine Management, with P.V.M. Bot as project leader (RIKZ-Den Haag), in co
operation with the North Sea Directorate and the department of Marine Ecology of the
NIOZ. The authors would like to thank the captain and crew on board of the RV. Pelagia,
the RV. Holland and the RV. Argus for their ambitious help during the cruise.
Thanks are also rendered to:
•
B. M. Berghuis, R. Daan, C. Winter (NIOZ-Texel) and the personnel of the North
Sea Directorate (RWS-Rijswiik) for assistance during the fieldwork.
•
M.S.S. Lavaleye for help with the identification.
•
H. Hobbelink (NIOZ-Texel) for designing the cover picture.
•
W. Schreurs and G. den Hartog (RIKZ-Middelburg) for analysing the sediment
samples.
•
J. Buijs (CEMOINIOO-Yerseke) for assistance with the data management.
•
M. v. Arkel for helping with financial questions.
•
K. Essink (RIKZ-Haren) the project manager for critically reading the manuscript.
Monitoring macrozoobenthos North Sea 1997
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-
Monitoring macrozoobenthos North Sea 1997
Tables and Figures
Tablel a.
Stati
Monitoring macrozoobenthos North Sea 1997
neW [
DOG ii
DOG 2
DOG 3
)Ies:
Pag
DOG 4
5.1
DOG 61
DOG 7a I
DOG
1(a/b)
2
3
Overview of the geographical position, date, depth and sediment composition of
the survey in 1997.
Mean values of abiotic and biotic parameters of the 4 distinguished areas in 1997.
List of the macrobenthos species found on more than 15 % of the stations in 1997.
-23-25-.
-26-
ures~
2
3
4
5
6
7
8
9
10(a/b)
1 I(a/b)
12(alb)
13(a-c)
14
15
16
17
19
20(a-d)
21
22
i
oysj
4
oys~1~~~
Sampling locations of the BIOMON survey in 1997.
Spatial distribution of the median grain size (pm) of the sediment in 1997.
Spatial distribution of the mud content (%) of the sediment in 1997.
Depth (m) of the 100 location sampled in spring 1997.
Temporal patterns of the median grain size (pm) in the period 1986 -1997.
Temporal patterns of the mud content (%) in the period 1986-1997.
Spatial distribution of the Hill0 diversity (number of species per box) of the
macrobenthos in 1997.
Spatial distribution of the total density (ind./m2) of the macrofauna in 1997.
Spatial distribution of the total biomass (g AFDW m2) of the macrofauna in 1997.
Temporal abundance patterns (ind./m2) of some selected macrobenthos species in
the period 1986-1997 found at the southern Dogger Bank.
Temporal abundance patterns (ind./m2) of some selected macrobenthos species in
the period 1986-1997 found at the Oyster Ground.
Temporal abundance patterns (ind./m2) of some selected macrobenthos species in
the period 1986-1997 found in the Offshore area.
Temporal abundance patterns (ind./m2) of some selected macrobenthos species in
the period 1986-1997 found in the Coastal area.
Temporal patterns of the Hill diversity (number of species per box) of the
macrobenthos in the period 1986-1997.
Temporal patterns of the Shannon-Wiener diversity in the period 1986-1997.
Temporal patterns of the Simpson index in the period 1986-1997.
Temporal patterns of the total macrobenthos density (ind./m2) in the period 1986-
-
-
-27-28-29-30-31-32-33-3435
OYS 6
OYS Z
OS’S 10
oS’s ii
OYS 12
OYS 13
OYS 14
OYS 15
OS’S 16
-360v’s 19
-38-40-42-
OS’S
0’S
OS’S
OS’S
OS’S
OS’S
20
21
22
23
24
25
-45OS’S 28
-46-~~-
oS’s 29
~ 30
-48-
os’s 31
1997.
18(a-d)
OYS
OYS 2 1
OYS~ 3
The density (md. m ) of the macrobenthos taxa in the period 1986-1997 found at -49the Dogger Bank(a), Oyster Ground(b), Offshore(c) and Coastal area(d).
Temporal patterns of the total macrozoobenthos biomass (g AFDW/m2) in the
-53period 1986-1997.
The biomass (g AFDW/m2) of the macrozoobenthos taxa in the period 1986-1997 -54found at the Dogger Bank(a), Oyster Ground(b), Offshore(c) and Coastal area(d).
DECORANA ordination of the combined datasets from 1986-1997.
-58DECORANA ordination of the 4 distinguished areas using the data of the period
-591986-1997.
OS’S 32
OS’S 33
OS’S 34
OS’S 35
&~
oS’s 39
OS’S 40
OS’S 41
0YS142
I
I
Table 1 a. Station number, position, date, depth and sediment composition of the BIOMON survey in spring 1997
Station (name)
new
previously
DOG 1
Dog ES
DOG 2
Dog D3
DOG 3
ICES 97/5M38
DOG 4
T5 235
DOG 5
Dog CS
DOG 6
Dog C6
DOG 7
ICES 87/SM 37
OYS 1
MZ 1.3 91
OYS 2
MZ 9-1 91
OYS 3
ICES 88/SM 39
OYS 4
Dog B5
OYS 5
MZ 8-3 91
OYS 6
Dog E2
OYS 7
MZ 2-1 91
OYS 8
MZ 12-4 91
OYS 9
MZ 15.1 ‘93
QYS 10
MZ 1.1 ‘91
OYS 11
MZ 12-1 91
OYS 12
MZ 5-4 91
OYS 13 ICES 78/SM 31
OYS 14
MZ 5-3 .91
OYS 15
MZ 5-1 91
OYS 16
MZ 3-4 ‘91
OYS 17
MZ 17-2 ‘93
OYS 18
MZ 10-2 ‘91
OYS 19
Dog B2
OYS 20
Dog Al
OYS 21
TS 50
OYS 22
MZ 1-4 ‘91
OYS 23
Dog C3
OYS 24
MZ 11-3 ‘93
CYS 25
MZ 2-3 ‘91
OYS 26
MZ 8-5 91
OYS 27 ICES 70/SM 60
OYS 28 ICES 42/SM 19
OYS 29 ICES 68/SM 32
OYS 30
MZ 1 1-1 93
O’i’S 31
MZ 19-2 ‘93
OYS 32
MZ 6-5 ‘91
OYS 33
MZ 4-1 ‘91
OYS 34
MZ 16-3 ‘93
OYS 35
MZ 18-3 ‘93
ON’S 36
META 2
ON’S 37
TS 100
ON’S 38 ICES 34/SM 20
ON’S 39 ICES 69/SM 30
ON’S 40 ICES 89/SM 58
OYS 41
RHC 4/Dog C4
ON’S 42
R 70
Geographical position
£
N
04°03’OO’
03°38’30”
03°30’OO”
03°09’26”
03°14’OO”
03°05’OO”
03°00’OO”
03°25’3o’
05°32’30’
04°00’OO”
02°56’OO”
04°55’OO’
04°2248”
04°18’OO”
04°54’OO”
03°37’SO”
03°42’aO”
05°10’OO”
04°26’OO”
03°3000’
04°44’30”
04°21 ‘20’
05~03’00”
03°25’OS’
05°54’OO”
03°19’OO’
02°51’Sl”
04°46’03’
03°38’30”
03°22’OO”
03°29’46”
04°32’OO”
04°47’30’
05°00’OO”
03°30’OO”
03°00’OO”
03°18’21’
04°09’06”
05°05’OO”
04°03’OO”
04° 1 637”
03°52’24”
04°30’OO”
04°20’27”
03°00’OO”
04°00’OO”
05°00’OO”
03°17’36”
06°12’Sl’
f
55°28’18’
55°l00O”
55°15’oO
55°10’14”
54°54’42”
54°57’06”
55°00’OO”
54°23’OO”
54°1 130”
55°00’OO”
54°3300
54°01’lO”
55°18’24”
54°5300”
53°44’40”
53°45’20”
54”39’OO”
53°5530”
54°10’OO’
54°45’OO
54°20’OO’
54°2830”
54°38’30”
54°00’21”
54°1 120”
54°2000”
54°05’OO’
53°46’04”
54°18’30”
54°49’24”
53°3000”
54°39’OO’
53°55’20”
54°30’OO”
53°45’OO”
54°30’OO”
53°31’30”
53°50’42”
54°15’30’
54°16’OO”
53°37’40”
53°51’31’
53°4205”
54°09’04’
53°30’OO”
54°30’OO”
55°00’OO”
54°51’42”
54°07’03”
Date
04103/97
04/03/97
04/03/97
04/03/97
05103/97
05/03/97
05/03/97
02104/97
06/03/97
04/03197
02/04/97
06103/97
04/03/97
04/03/97
06/03/97
08/04/97
05/03/97
06/03/97
02/04/97
05/03/97
05/03/97
05/03/97
05/03/97
08/04/97
06/03/97
02/04/97
08/04/97
06/03/97
02/04/97
05/03/97
09/04/97
05/03/97
06/03/97
05/03/97
08/04/97
02/04/97
09/04/97
02/04/97
06/03/97
02/04/97
02/04/97
08/04/97
08/04/97
02/04/97
08/04/97
05/03/97
04/03/97
05/03/97
06/03/97
Sediment
Depth Cm) Med. Gr. Size (pm) Mud (%)
30.0
37.0
28.0
30.0
36.0
22.0
24.5
44.7
40.0
49.0
32.6
43.5
47.0
51.0
36.5
35.8
45.0
40.0
46.8
45.0
47.0
51.5
47.0
40.6
38.1
47.2
50.1
38.6
43.3
42.0
31.7
50.0
42.1
44.0
33.9
35.0
33.1
41.2
45.3
47.0
35.1
37.9
37.2
47.9
31.8
46.0
41.0
39.0
33.3
213
175
207
191
172
197
195
110
189
112
135
127
141
87
167
178
112
102
96
111
132
95
133
178
199
116
180
107
137
113
130
101
131
165
192
122
124
132
150
102
113
153
99
‘
0
0
0
1
0
0
0
6
0
3
1
7
1
15
10
0
4
25
10
3
4
9
9
0
0
4
7
17
3
4
2
14
7
7
0
1
6
2
6
6
12
1
23
-
-
142
113
144
145
226
3
4
2
1
0
el b. Station number, position, date, depth and sediment composition of the BIOMON survey in spring
Station (name)
ew
•reviousl
fl MZ 18-2 ‘91
fl Z VIA-i 2-25-2
:3 MZ VA-i 2-25-3
:4
MZ 16-3 91
:5
MZ 14-1 ‘91
Geographical position
Date
05°59’OO’
06°06’25”
06/03/97
9C
03/03/97
‘89
05°49’37”
03/03/97
04°5730
53°40’OO”
08/04/97
04°22’30”
53°2900
02/04/97
MZ IIA-12-25-2 89
04°26’32
09/04/97
:7 MZ IA-25-40-4 ‘89 04°i822”
09/04/97
53°0i 30”
09/04/97
F8 MZ C-40-65-4 88 04°00’30”
04°1350
52°4920
07/04/97
F9 MZ B-25-40-2 ‘88
52°45’40”
09/04/97
F 10 MZ W.40-65-3 ‘88 03°50’30”
MZ 10-4 ‘92
03°31’iS’
53°1700”
09/04/97
F 11
MZ 9-2 ‘92
03°23’30’
53c0355”
09/04/97
F 12
MZ 9-1 92
03°i 136”
53~02’58”
09/04/97
F 13
MZ 8-2 ‘92
09/04/97
F 14
MZ 8-5 ‘92
09/04/97
F 15
ICES 20/SM 3
03°30’OO”
52°45’OO’
01/04/97
F 16
MZ 6-2 ‘92
03G1 21 2”
52°2743’
03/04/97
F 17
MZ 6-1 ‘92
52°20’25”
03/04/97
F 18
MZ 1-1 ‘92
03°24’42
52°15’lO”
03/04/97
F 19
ICES 15/SM 5
03°30’OO
52°15’OO’
03/04/97
F 20
03°00’OO”
52°00’OO”
10/04/97
F 21 ICES 12/SM 10
03°59’15”
52°16’30
01/04/97
F 22 MZ T-25-40-3 ‘88
52°23’08’
01/04/97
F 23 MZ N-i 2-25-1 ‘88 04°09’50
/
03°42’58
52°00’OO”
02/04/97
F 24
/
—
02/04/97
F 25 ___________
/
10/04/97
‘F 26
/
03°14’28”
10/04/97
‘F 27
/
10/04/97
‘F 28
A 50
53°57’14”
06/03/97
‘F 29
•‘.
•
TS 30
08/04/97
‘F 30
•
.
META 1
09/04/97
‘F 31
N 30
01/04/97
‘F 32
.)CL1 ,Mep~.-flnWI.~
N 50
01/04/97
‘F 33
N 70
01/04/97
W
30
03°06’49
10/04/97
‘FEE
W 70
02°40’45
51 o57!25~
10/04/97
‘FEE
Z VIA-05-12-i ‘8%.
03/03/97
)A
Z VA -00-05-5 ‘89
03/03/97
MZ W-00-05-5 ‘88
52°32’SO
07/04/97
52°50’OO
07/04/97
)Afl MZ C-00-05-5 ‘88 04°40’OO”
MZ IB-00-05-5 ‘89
04°41’20”
53°03’23
03/03/97
03/03/97
DAfl MZ VIB-00-05-3 ‘89 06°1i’iO’
R 3
03/03/97
DA 7
TS 4
05°09’02”
53°24’54’
03/03/97
DA 8
ICES 21/SM 1
04°30’OO
52°45’OO”
07/04/97
DA 9
04°24’20
52°15’36
01/04/97
DA 10
04°18’Ol’
52°17’41
01/04/97
DA 11
03°23’lS”
51°37’04”
10/04/97
GA 12
03°36’02”
51 O4~•~3”
18/04/97
GA 13
03°48’48”
51°47’26’
18/04/97
GA 14
03°55’09
51 055’20”
10/04/97
GA 15
9
Sediment
Med. Gr. Size Wm)
53G51’30”
53°3729”
53°36’40
0
0
fi
‘I
4
-t
I
+
*
C
C,
I,
a
a
4.
E
cCI.
CC
C
C.
4-
C
-C
-c
C
Ct
C
4-
C
Cc
C
U,
a,
D
Cv
>
C
Cv
0)
0)
-o
Cv
I-
Table 2. Mean values of abiotic and biotic parameters of the 4 distinguished areas in 1997 (CV.: coefficient of variation
AREA
UI
No. of stations
Median Grain Size (pm)
Mudcontent(%)
Depth (m)
Diversity:
No. of total species
No. species per core
Shannon- Wiener diversity
Simpsons dominance
No. individuals (ind.Im9:
Crustaceans
Echinoderms
Molluscs
Polychaetes
Miscellaneous
TOTAL DENSITY
Biomass (p AFDWIm2):
Crustaceans
Echinoderms
Molluscs
Polychaetes
Miscellaneous
TOTAL B!OMASS
south.Dogger Bank
C.V.
192.9! 0.08
01: 380
29.6! 019
35~~
.jom
0.08! o.~
549.6:
21~
234.1
0.52
ole!
1.97:
1.52!
0.65
090
017
0.51
1.04
0.98
~
29.l~o2
i6.4a~3o
0.13!
056
0.18!
052
150.8:
0.73
416.1:
i.~
~
412.8! 1.11
640.5: cm
197.9! 0.82
2038.0: 051
2.50!
5.48:
0.44!
1.98
1.62
155
0.48
Coastal area
i5
219.3!
05
12.2!
c.v
022
414
0,44
47
1?.
.18:0.17
75.2! 1.68
~jj~o
55.3! 1.58
1149.6: 0.78
0.22!
6.15:
2.31!
0.25: os~
134.6:
4.9j
205.8!
8.8!
1514.7:
1.44
1.23
1.76
0.90
3.31
2.87
0.04
0.38:
31.87!
121
36.00!
Iii
2.55
1.79
1.36
1.19
~
98
:1.34
5.52!
Offshore area
JC.V.
soi.fi 0.26
00 000
28.6! 014
~:9Ll~
1~j~8
232.0!
2376.4:
Oyster Ground
42
Jc.v.
135.1! 0.24
58: 104
41.8! 0,14
12.83!
098
11.63!
s.d/mean).
Table 3.
Average density and biomass with standard deviation (st.dev.) of the macrobenthos
species found in more than 15 % of the stations in 1997.
Species name
%
Density
st. dev.
Biomass
st. dev.
SPIOPHANES BOMBYX
SCOLOPLOS ARMIGER
MAGELONA PAPILLICORNIS
SPIO FILICORNIS
BATHYPOREIA ELEGANS
67
64
63
51
49
77.1
56.5
153.3
59.6
92.3
131.0
110.8
347.2
163.7
246.3
0.0560
0.1234
0.1837
0.0189
0.0277
0.1191
0.2494
0.5948
0.0464
0.0739
NEPHTYS HOMBERGII
NEPHTYS CIRROSA
GONIADA MACULATA
NATICAALDERI
CHAETOZONE SETOSA
46
43
42
41
40
14.6
26.3
12.9
15.7
14.0
21.3
39.2
20.4
26.3
25.9
0.3292
0.1487
0.0217
0.0382
0.0055
0.6590
0.2777
0.0568
0.1621
0.0106
ECHINOCARDIUM CORDATUM
MYSELLA BIDENTATA
PHOLOE MINUTA
AMPHIURA FILIFORMIS
UROTHOE POSEIDONIS
40
39
34
32
31
12.9
53.4
32.9
104.5
43.8
26.3
128.2
80.3
241.2
107.9
3.2346
0.0109
0.0055
0.7900
0.0131
8.2019
0.0257
0.0139
2.3000
0.0324
MONTACUTA FERRUGINOSA
POECILOCHAETUS SERPENS
BATHYPOREIA GUILLIAMSONIANA
ABRA ALBA
SCOLELEPIS BONNIERI
28
27
26
25
24
16.7
9.4
27.2
9.7
6.9
53.7
30.6
70.9
23.5
32.6
0.01 24
0.0074
0.0095
0.0100
0.0561
0.0342
0.0313
0.0268
0.0600
0.1360
TELLINA FABULA
HARPINIAANTENNARIA
NUCULATURGIDA
ETEONE LONGA
CALLIANASSA SUBTERRANEA
24
23
23
22
21
13.6
14.9
12.9
4.5
9.8
37.7
41.5
36.6
9.9
22.8
0.1028
0.0045
0.0386
0.0033
0.3619
0.6536
0.0125
0.1225
0.0139
1.0642
LANICE CONCHILEGA
NOTOMASTUS LATERICEUS
OPHIURAALBIOA
VENUS STRIATULA
CYLICHNA CYLINDRACEA
20
20
20
20
19
26.5
13.5
10.2
6.9
8.8
180.0
46.8
27.1
19.2
27.8
0.3324
0.2794
0.1074
0.0592
0.0125
1.5786
1.3547
0.3455
0.3901
0.0469
SPISULA SUBTRUNCATA
UROTHOE BREVICORNIS
CORBULA GIBBA
PERIOCULODES LONGIMANUS
ARICIDEA MINUTA
19
19
18
18
17
18.1
18.7
29.0
5.6
7.5
100.3
55.0
235.4
13.9
26.0
1.1744
0.0066
0.01 05
0.0017
0.0008
10.9534
0.0201
0.0422
0.0042
0.0025
CINGULA VITREA
CULTELLUS PELLUCIDUS
DIASTYLIS BRADYI
EUDORELLATRUNCATULA
OPHELIA LIMACINA
16
16
16
16
16
13.2
3.7
3.5
6.3
6.0
59.2
10.5
10.6
18.8
22.5
0.0026
0.0134
0.0021
0.0013
0.0376
0.0090
0.0593
0.0057
0.0038
0.1675
PSEUDOCUMA LONGICORNIS
16
4.4
12.6
0.0009
0.0025
3
2
4
a:
a.
4
•
$
;.
*
Sn’
63•
7
0
$
14
$5
p
4
31$
R
ant Bbno.t#oe*ig
1$
pMq
flee
a
n t$%
• cwsro.v.nle
• caee(~q~
‘C ~
44
Fe 1. LocatIons of the nnptg statIons w*fli hate ban visited awMg the swvey hi lflZ
53
52
0
Median grain size (um)
•
•
<175
175-250
• 250-300
• 300-350
•
>350
Fig. 2. The median grain size (pm) of the sediment in 1991
28
Fig
Median grain size (urn)
<175
175-250
250 300
300 350
> 350
-
-
Fig. 2. me median grain size (pm) of the sediment in 1997.
28
Mud content (%)
•
<2
• 2-5
• 5-10
• 10-15
•
>15
Fig~ 3. The mud content (%) of the sediment in 1991
29
Depth (m)
•
<20
• 20-25
•
•
•
•
25-30
30-35
35-40
40-45
•>~~
Fig. 4. The water depth (m) of the sampling stations In 1997.
30
230
Median grain size (pm)
230
Dogger Bank
Dogger Bank
220
220
~ 210
.3
210
200
190
100
180
170
170
ISO
160
~ ~ØS
400
~n~5S~g9O~g9’ ~
400
Oyster Ground
Oysier Ground
350
350
300
S
~ 250
250
200
150
ISO
100
100
50
50
s
~ ~a9
600
600
Of fshore area
Offshore area
470
470
•I.i
S
a
340
2
340
I
210
II
210
00
eo
375
375
4e5~,ga1 ~
S5~Ø6~591
Coasiai area
Coasiai area
325
325
~ 275
275
S
a
La
225
2
175
125
•~<t~tfH
~ø8,≠e~ø1
,5aS~1e~~5
225
175
125
~ ~øS
Yea,
Year
Fig. 5. Temporai patterns of the median grain size (pm) in the period 1986-1997
3.4
Mud content (%)
3.4
Dagger Bank
Dagger Bank
be
25
2.8
22
2.2
16
1.6
1.0
10
C
S
04
-02
~e~~e2S*~ ,~eb~es,
-0.2
~rrrII
~aa’søt~8ab~øA,e#1b*~a& ~e0
35
35
Oyster Ground
Oyster Ground
25
25
be
‘I
Is
§
5
-5
10
IC
III
Offshore area
Of f shore area
a.
£
S
a
8
6
6
a
4
4
2
2
0
-2
~ ~baS
-2
Is
15
coastal area
coaslal area
11
Ii
7
7
be
S
S
3
—1
Year
Year
Fig. 6. Temporal patterns of the mud content (%. 16-63 pm) in the period 1986—1997
DWerslty (HiII-0)
•
<10
• 11-15
•
16-20
•
21-25
•
26-30
•
>30
Fig. 7. The number of species per sample (Hill-O) of the macrobenthos in 1997.
33
52
0
4%
Density (indJm2)
•
<500
• 500-1000
• 1000-2000
• 2000-3000
• 3000-4000
•
>4000
FIg. 8. The total density (indJrn2) of the macrozoobenthos in 1997.
34
FIg. 9
Blomass (gAFDW/m2)
•
<5
• 5-10
• 10-20
• 20-40
• 40-80
. >80
Fig. 9. The total biomass (g AFDW/m2) of the macrobenthos In 199Z
35
species density
Dogger Bank
050
050
750
750
650
650
‘N
!!!,,!!!!
Bathyporeia elegans
550
!550
450
Ia
350
250
•
•
150
~
50
-50
~
~~
600
600
II
500
500
4400
400
300
300
~200
200
I~•I!!I!!
—
100•
-
°.—_-_
0
Lanice conchilega
-100
-100
700
700
-~
~ ~q~s
600
Magelona papillicornis
600
-
6
~500
500
400
400
S
300•
200
$200
10
100
0
~
700
I
~
II!!I~II
~gte.~@0~ggN \ggZ~qgS~oM$9l
~
700
600
600
~500
500
Mysella bidentala
N
400
400
~300
300
~200
200
5i00
100
0
0
I
-100
~
YEAR
YEAR
Fig. 1 Oa. Temporal abundance patterns (md/rn 2) of some selected species between 1986—1997.
36
Dogger Bank
—
species density
120
120
94
94
~!!!•~~!!
Nalica alden
68
42
Is
-~
-10
~
~
200
200
Nephtys cirrosa
.
150
150
I
100
:ir
~
~
I
I
3000
3000
2000
2000
1000
1000~
0
0~
-1000
1000
1000
‘000
750
780
~560
560
~340
340
Spiophanes bombyx
~
~
~
120
Tellina fabula
l2O~
-100
-IOU
\gSS.Lg9O\o9’\9~g95~99ki99S\9ø¼g%1
Year
Year
Fig. lOb. Temporal abundance patterns (md/rn2) of some selected species between 1986 1997
Oyster Ground
—
species density
4250
4250
3250
3250
2250
2250
-
Amphiura filifornils
E
;125o
:
•
1250
1250
250
-750
-750
325
325
225
225
125
125
25
25
-75
-75
200
200
155
155
110
110
65
65
-
callianassa subterranea
0
E
I
20
~
~
*
—
:
—
20
•
—
-25
-25
,~~tS~i& ~
~,
~ ~gØ
2000
2000
1550
1550
1100
650
-
200f
-250
Echinocardium cordatum
-
~
~
I
1100
I
650
i~ i
!!!!IIIIIIII
Year
Magelorla papillicornis
~0
200
-250
Year
Fig. 1 la. Temporal abundance patterns (md/rn2) of some selected species between 1986—1997.
Offshore area
species dens ty
—
2000
2000
1700
1700
1400
1400
2
1 100
1100•
a
a
a
800
800
500
500
&
8
200
:
•
~
—
i
-lao
,ae~1a*,aal ~
I
100250
195
195
140
140
85
85
*
~
Ba thyporeia elegans
200
250
30
—
Echinocardium cordatum
30
•
-25
,≠~a*,—_a1 ~
-25
10000
10000
7900
7900
5800
5800
3700
3700
1600
1600
-500
\*3~*_~~Ø1 ~
-500
8000
8000
-
Lanice conchilega
o
0
Magelona. papillicornis
0
6000
6000
4000
4000
2000
2000
~
0
-
-2000
~qe6,≠~e1 ~ ~a@
Year
0
_:LliiLl
-2000
Year
Fig. 12a. Temporal abundance patterns (md/rn2) of some selected species between 1986-1997
Offshore area
—
spec es density
150
150
115
115
60
60
46
.
Natica alder
45
.
10
-25
-25
325
225
250
250
1175
175
Nephtys cirrosa
100
25
-50
~0’
24000
24000
18800
16600
13600
13600
8400
6400
3200
3200
-2000
-2000
600
800
600
600
p400
400
Spiophanes bombyx
6
S
‘~
:4,
Tellina labula
C
1200
.
0
.
.
—
—
~
-200
S
0
200
0
~~Li
—200
Year
Year
Fig. 1 2b. Temporal abundance patterns (md/rn2) of some selected species between 1986 1997
Coastal area
-
species density
450
450
350
Bathyporeia slogans
350
-
E
250
250
I
ISO
S
50
50
-50
-50
.
,qsb~*i~~&
-
~
100
100
60
60
40
Echinocard~um cordatum
40
•
2:
-20
-20
,*~~2*i*1 ~
12000
12000
10000
10000
8000
8000
6000
6000
4000
4000
.
2000
0-2000
Lanice conchilega
:
•
•
0
II
-2000
-
I,
-
I
I..
2000
~Ø6~g*~Ø1 ~ ~gIt
17000
17000
13300
•
Magelona papillicornis
13300
9600
9600
5900
5900
2200
2200
;
~•
-1500
~ee~~eZe~eeI ~
Veer
-1500
Veer
Fig. 13a. Temporal abundance patterns (md/rn2) of some selected species between 1986-1997.
Coastal area
species density
750
750
550
a
•
350
—
[.4ysella bidentata
550
350
0
150
1~50
00
_~4..g~:
-250
•!!!~!~!!!!!
~ fl
~ ~a0S
90
-50
-250
90
•
70
Natica alden
70
50
50
•
*
t
500
500
400
400
*
300
•
Nephtys cirrosa
300
S
;200
•
0
~
-100
100•
0-A~
4cQ)j1
-100
200
I
~aø,Ø0,~al ~ ~S
275
II
200
*
-200
275
p
S
pp
Nephtys hombergii
-
175
175
j
-:
~ ~ga5
Yoar
Year
Fig. 1 Sb Temporal abundance patterns (md/rn 2) of some selected species between 1986—1997
Goasta area
spec es density
300
300
250
250
•~&
200
%‘
200
-~
~
150
150
[00
100
~
50
5°
C
0
50
~
25000
III
-50
25000
20000
20000
15000
15000
10000
10000
5000
5000
E
S
0~.
a
Pectinaria koren
Spiophanes bombyx
0
L0
5000
-5000
-10000
%0~0Oi@~ ~
10000
5500
5500
4500
4500
~ 3500
3500
Spisula subtruncata
,~
It
g2soo
2500
Ie
~
1500
.~
1500
to
500
500
.
—.:-..
::~-.•-:,
-500
~
-500
1100
1100
900
900
~700
700
~
500
~
500
:‘~
300
100
-100
~ .0
Year
-100
Tellina fabula
x
-I
~
.ets0S.eets0O%0~sg%SaO~04,0b~0Si0l
Year
Fig. 1 3c. Temporal abundance patterns (md/rn2) of some selected species between 1986—1997
HiII(O)
—
divers ty
47
47
Dagger Bank
37
a
27
Dagger Sank
~Jt
37
27
17
17
50
50
Oyster Ground
Oyster Ground
40
40
A
A
A
30
20
10
!!!!IIIII~
$1
~
10
40
40
—
Oil shore area
Offshore area
I
30
0
0
Coastal area
Coastal area
30
30
20
20
10
10
0
Year
Year
Fig. 14. Temporal patterns of the species richness (Hill—O) between 1986—1997.
Shannon—Wiener diversity
4-0
40
Dogger Bank
Doggor Bank
as
35
3o.~
~2.5
25
2
L0
20
2.0
-
15
15
~Ø5.r.tb~Øl t~≠
4
~ ~S
4
rrrrr.r.rrr_
Oyster Ground
Oyster Ground
a
2~
,~_~a)1øo,*l ~
Offshore area
Offshore area
2
~q~.jatôj*l e5~ ~
35
as
I,
Coastat area
Coastal area
~25
-
25
j15
15
as
05
T
~e~gs1 ~ ~
Year
~eS~g69~e9’ ~@2s~3~g°
Year
Fig. 15. Ternporaf patterns of the Shannon-Wiener diversity between 1986 1997
Simpson
0.5
diversity
—
as
PP
Dogger Bank
0.4
Dogger Bank
S
aS
~03
£
0.2
01
0.1
00
,*~e*,q& ~
0.0
0.7
0.7
ii
Oyster Ground
Oyster Ground
0.6
08
as
as
:
~0A
j
~0.3
0.4
0.3
a
E: ~E—E-:EtTtTtH E
11
•pppipp.piip
1,1
Of fshore area
a9
Offshore area
0.9
•
a7
0.7
•
a
F
5 as
a
•
•
-al
•
as
alt
~
~~
ao
a9
Coastal area
Coastal area
a?
ay
as
o.s
S
.4-,
al
I
.
•
a3
al
-0 ~
~*~Q*~t& ~qat~e~e~ e~ez~Ø~,ea~sØ5,Øe,eel ~a$
Year
Year
Fig. 16. Temporal patterns of the Simpson index of dominance between 1986—1997.
Total density
10000
10000
Dogger Bank
Dogger Bank
1000
1000
100
~atb,c
100000
100
~g9b~96~gQl
100000
-
Oyster Ground
‘0000
Oyster Ground
10000
1~.
100
~ ~
100000
1000
100100000
Offshore area
10000
Offshore area
10000
1~.
100
~ea6.Lgt,*’ ~ ~*
100000-
1000
100
,gø
100000-
Coastal area
Coastal area
10000
10000
1000
~1000
100
100
10
10
-
~$~.ae~*øi ~
Year
Year
Fig. 17. Temporal patterns of the total macrobenthos density (md/rn 2) between 1986 1997
Dogger Bank
10000
taxa density
iii
10000
Polychaeta
i
Polychaeta
1000
100
100
~ ~t
10000
4
11411111111
,g@~g90~g9’ ~
10~
Crustacea
I
Crustacea
l000._______~\~:.
100
--
100
10
~*~a,,s1 ~lø,~e
10000
1000~
~
9%9ø,4~S~Øl ~ø
pip
10
10000
Molluscs
pp
Mollusca
1000
l~
100
100
10
10
5
9
111111111
~
1000
pip
pp.ppp~pi
1000
Echinodermata
10
ppp..pppi
Echinodermata
10
~pgPJppgOppØ~ ~
Year
Year
Fig. 18a. The density (md/rn2) of 4 macrobenthos taxa between 1986—1997
Oyster Ground
10000
—
taxa density
10000
i
Polychaeta
t
1000
1000
IOU
‘00
bOO
1000
Crustacea
:
100
100
10
10
C
N
a
,geS~eta,eSl ~
~Ø%qa6~~ø,gG1
~ee~
10000
10000
Mollusc
Molitisca
1000
C
N
1100
H
10
100
10
1—
~,a*b~eSl
~
10000
10000
-
[chinodermata
Echinoderinata
1000
1000
1100
100
10
10
C
N
~al~,et8~øl ~
Year
Veer
Fig. 1 Sb. The density Kind/rn 2) of 4 macrobenthos taxa between 1986 1997
Offshore area
100000
—
taxa density
100000
-
Polychaeta
-
Polychaeta
10000
10000
1000
bOO
100
100
10
10
E
N
Os
0
50000
10000
Crustacee
a
Crustacea
1000
1000~•
N
till
10
10
,eø
10~
10000
-
Mollusca
1000
1000
S
a
•
N
100
100
10
10
1000
1000
Lchinodermata
~chin
bOO
100
10
10
Year
ermata
Year
Fig. 18c. The density (md/rn2) of 4 rnacrobenthos taxa between 1986—1997,
Coastal area
taxa density
100000
100000
Polychaeta
Polychaeta
10000
10000
‘1000
100
100
10
10
10000
10000
Crus~acea
Crustacea
~ioooN~Jç
10000
________
10000
Mollusca
Mollusca
1000
1000
100
100
10
10
0
1
~ ~~1g
1
~ ~ØS
1000
1000
Echinodermata
100
Echinodermata
•
100
10•
Year
Year
Fig. 18d. The density (md/rn2) of 4 rnacrobenthos taxs between 1986—1997
Total biomass
30
30
Dogger Sank
~2O
20
10
10
0
0
~ ~eb~,6~Ø1,Ø%
60
Oyster Ground
60
~
30
o
0
jt~6%#6%~1 ~
175
III
175
Of tshore area
Offshore area
145
145
115
115
85
65
25
25
-5
~a6~*.~s1 ~ fi,*~\4a2~ a2~ae,~a~,e*,e%l ~aa~
-5
400
400
Coastal area
Coasta area
330
330
~ 260
260
)lgo
leo,
120
.
120
o
:~
•
:.:..
so
I~I.IlII
-20
,~eS~aeB,e& ~ ~aQ~
Year
___________________
-20
Year
Fig. 19 Temporal patterns of the total biomass (g AFDW/m2) between 1986—1997
Dogger Bank
—
taxa biomass
5
5
Polychaeta
Polychaeta
4
4.
0
S
2
0
0
~l
~
0.9
0.9
Crusiacea
Crustacea
07
0.7
0.5
0
0.3
0.1
-0.1
~ ,ø•
26.0
ii
~J
26.0
Molluscs
Mollusca
19.4
19.4
C
12.8
62
•1.3
-7.0
-7.0
20.0
20~
Ecririodermata
Lchincdermata
15.6
15.6
A
a
-0.4
11.2
112
0
GB
2.4
-2.0
e~*~Ø1 ~1 ~ .~S
Year
Fig. 20a The
Year
biomass (g AFDW/m2) of 4 macrobenthos taxa between 1986—1997.
Oyster Ground
taxa biomass
40
40
Polychaeta
Polychaeta
33
33
5
5E26
26
19
19
9
o
12
:
iS
a
G
II
*
a
S
12
:~:
‘ass
40
40
Crustacea
Cnjstacea
31
31
22
22
9
~4a
a
13
•
•
IS
jje~
*
~-HHHt~:
~~;a5~ ~
60
60
p
Mollusca
Molluscs
47
47
34
21
8
a.
-5
~~
-5
50
50
p
Echinodermala
Echinoderma ta
39
•
17
a
Year
a
39
•
•
S
~l
•°
:1
3
28
I
17
Year
Fig. 20b. The biomass (g AFDW/m2) of 4 rnacrobenthos taxa between 1986—1997.
Offshore area
—
taxa biomass
30
30
Polyohacta
Polychaeta
25
25
~20
-
20
15
-
IS
0
~
0
-5
-5
4fl
40
Crustacea
Crustacea
3,1
-
22
3,1
22
C
0
t~
13
-
a
CA
.
:
•
•
I i ~ ~ I I I
-Os
IllIlIllI
‘It
~ ,Øt
175
1,3•
:~
175
i,,
Molkisca
Mollusca
145
-~
-
115
145
‘
115
85
-
85
0
1
55
25
25
~
,*sG5e~ø1 ,~5S~Ø
I
I I
I
70
60
-5
O.eQ%~Øt,glZiØ%e#isB~Øl ,Ø
70
Echinodermata
50
50
50
40
40
30
30
20
20
10
10
Echinodermata
0
I
0’
0
10
~ ,e*
Year
-10
Year
FiQ. 2Cc. The biomass (g AFDW/m2) of 4 macrobenthos taxa between 1986—1997.
Coastal area
taxa biomass
—
100
100
Polychaeta
79
Polychaeta
.
79
-
58
58
‘9
a
37
.
37
.
,~,Q2&,ø1 ~
1.5
1.5
ii,,,,
11
C
—
Crustacea
Crustacea
II
.
0.7
0.7
1e5b_~ee1
400
~
400
iiitii.pi,j
Mollusca
315
315
-
230
230
*
S
145
60
.
::
,:;
-25
‘‘‘‘‘‘‘•~‘‘
~ ~e≠
40
145
60
-25
40
Echinodermat~
Echinoderm~ta
30
20
(9
10
-10
30
•
•
20
,
:
‘
‘
~~‘‘‘‘~‘‘‘‘•
Year
10
-10
Year
Fig 20d. The biomass (g AFDW/m2) of 4 macrobenthos taxa between 1986—1997.
-
•
-
•
•
1990
I
-50
-100
1995
I
A 1996
1993 1994
1992uhLA
A
Dogger Bank
Oyster Ground
Offshore area
Coastal area
1986 1991 A1997
A
*
•
•
*
1994
1992
0
I
•
50
I
•1986
•1991
100
I
1993
~1996
•j995
1997.e1989
4988
•1994 •19921990
1986
1996 1988
l993~~
1991 t~1992 ~iggo
1997½~~~
*
1995
1989
1995%
1991*
1997
1993
**
)IE
1986
150
?IE
199C
•199o
(a)
Dogger Bank
150_I
1990
(b) Oyster Ground
Fig. 21. The DECORANA ordinaten of the combined datasets from 1986 (ICES-NSBS), 1988-1993 (MILZON- project)
and 1990-1 997 (Biomonitoring North Sea, this report).
100
-50
0
50
100
150
j
Ut
-
-
0
I
i2~!
50
I
*1989
1992 991
* *1
100
I
* 1988
I
150
I
I
I
150
I
250
—
300
I
*1990
Offshore area
200
(0)
100
1986
-
-100
-50
0
50
100
150
200
-50
-
0-
50
100-
150-
-50
1994
•1993
Icoastai area
.1992
(d)
-50
1995
0
0
50
50
1991
•1996
•1988
.1989
•1990
1993
1992
1995
1991
1997
1996
1994
100
•1986
150
1997
.
100
1986
Fig. 22. The DECORANA ordinaten of the 4 distinguished areas; the southern part of the Dogger Bank (a), the Oyster Ground (b), the
Offshore area (c) and the Coastal area (d) using the data of the period 1986- 1997.
*
*1994
* 1986
I
50
I
0
11992
•1991
•1995
1997
•1996
•1994
•1993
*1993
-50
-50-
0-
50-
100-
-50
0-
50
100-
SeO!pUeddV
£661 ~O5 ~PO~ so~uaqoozosonu ~uuopuoN
U
U
flU
N.
U.
n
U
N
.
a
U
N.
N.
ni mm m m hum m m ii, p1 m ill m m m ni m m m o C C
cccccc—1-1--1zzzzz000000000
fin
fiN
.1
U.
_
N
fiNn.
U
UUU
S
I
.
00
•
——nrJC,—.n
.
.
.
r
—
•
S
+
•
S
+1
•
.
-‘~°
ov:oJo:~’OVOOO.t
o ~ ~
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Appendix-i Biomonitoring 1997 (+=presence,
-
absence)
offshore area
;ies name
Code
TOPTERUS JUVENILE
TOPTERUS VARIOPEDATUS
E SPEC.
ILA VITREA
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JLA GIBBA
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ENSIS
4+
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Appendix-i Biomonitoring 1997 (+=presence,
absence)
-
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Appendix-i Biomonitoring 1997 (+presence,
-
absence)
pffshore area
9sname
1
2
S HOMBERGII
S INCISA
±
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RIA KORENI
ODES LONGIMANIJS
PEC.
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DA
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IEMOTA
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ATESALTAMARINUS
ATES ARENARIUS
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RVILLEA KEFERSTEINI
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Appendix-I Biomonitoring 1997 (+=presence,
Iffshore area
S.ecies name
~BAA ALBA
~BRA JUVENILE
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\MPELI5CA TENUICORNI5
•
0
•
-
0
-
0
-
0
28
29
3•
31
32
33
34
35
isi Code
I
kMPHARETE SPEC.
\MPHIURA ALIFORMIS
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I
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tNTHOZ0A SPEC.
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-
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-
+
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PLACOPHORA
RCTICA ISLANDICA
RGISSA HAMATIPES
RICIDEA MINUTA
STARTE TRIANGULARIS
STEROIDEA JUVENILE
STERIAS RUBENS
STROPECTEN IRREGULARIS
TYLUS FALCATUS
TYLUS SWAMMERDAMI
UTOLYTUS SPEC.
~.THYPOREIA ELEGANS
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VALVAE SPEC.
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27
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II
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+
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+
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IAETOZONE SETOSA
77
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ABRA JUVE
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ACRO BRAG
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ANAl GROE
ANAl JUVE
ANAl LINE
ANAl MACU
ANAl MUCO
ANTH OZOA
AONI PAUC
APHR ACUL
APHR JUVE
APLA COPH
ARCT ISLA
ARGI HAMA
ARIC MINU
ASTA TRIA
ASTE JUVE
ASTE RUBE
ASTR IRRE
ATYL FALC
ATYL SWAM
AUTO SPEC
BATH ELEG
BATH GUlL
BATH JUVE
BATH PELA
BATH TENU
BIVA LVAE
BRAN LANC
BRIS LYRI
CALL JUVE
CALL SUBT
CALL TYRR
CAMP GLAB
CAPI CAPI
CAPI TELL
CAPR ELLI
GAUL LERI
CHAE SETO
Appendix-i Biomonitoring 1997 (+presence,
I
38
name
iPTERUS JUVENILE
PTERUS VARIOPEDATUS
SPEC.
~ VITREA
‘IA CRANCHII
JLIDAE SPEC.
A GIBBA
hUM AFFINE
hUM SPEC.
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US PELLUCIDUS
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LIS BRADVI
LIS LAEVIS
RRUS GLAUCUS
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CARDIUM CORDATUM
CARDIUM FLAVESCENS
CARDIUM JUVENILE
CYAMUS PUSILLUS
US SPEC.
DSIA CLAPAREDII
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NSIS
PEC.
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JUVENILE
LACTEA
LONGA
ELLOPSIS DEFORM S
ELLA EMARGINATA
ELLA TRUNCATULA
• ALBA
SANGUINEA
CE SPINIGERA
INAE SPEC.
JS FLABELLIGERUS
NE HEBES
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DPODA SPEC.
ANA CIRROSA
~A ALBA
~A LAPIDUM
29
30
31
32
33
=absence)
Coastal area
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1:7
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Species
CHAE JUVE
CHAE VARI
CHON SPEC
CING VITR
CIRO CRAN
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CORB GIBB
CORO AFFI
CORO PHIU
CORY CASS
CULT PELt.
GLYCINDE
GLYCERA
GOLFINGI,
GOLFINGI,
GOLFINGI,
GONIADEL
GONIADA
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GYPTIS C,
HARMOn
HARMOTF
HARMOTF
HARPINIA
HARPINIA
HARPINIA
HESIONUF
:HIPPOMEC
HYDROZO
lONE THO
IPHINOE T
LAMPROP
LANICE CI
LANICE Jt
LEPTON S
LEUCOTH’
LEUCOTH’
LUMBRINE
LYSILLA L
MACOMA
MACTRA
MAGELOI’
MAGELOIS
MAGELOI’
MALDANII
MEDIOMA
MEGALUR
MICROPH
MODIOLU
MONTACt
MONTACt
MYRIOCH
MYSELLA
MYSIA UI’
NATICA A
NATICA J
NEMERTII’
NEPHTYS
NEPHTYS
L1i ICYLI CYLI
Lzjts DIAS BRAD
-
----4
-
-
an
-
-
-
-
-
-
-U
I
---~:::~+-4~-
fl-~
--4
*1
4,
-
DIAS LAEV
DIPL GLAU
DONA VITT
DOSI JUVE
DOSI LUPI
0051 SPEC
ECHI CORD
ECHI FLAV
ECHI JUVE
ECHI PUSI
ECHI URUS
EDWA CLAP
ENSI ARCU
ENSI ENSI
ENSI SPEC
ENTE ROPN
ETEO JUVE
ETEO [ACT
ETEO LOj~J
EUDO DEFO
EUDO EMAR
EUDO TR~4~J
EULI ALBA
EUMI SANQ~
EURY SPIN_
EUSY LLIN
EUZO FLAB
EXOG HE~J
EXOG Np4pJ
GARI Fg~J
GAST ROPPJ
GATT ci~J
GLYC ALB~J
GLYC [API
-4,--
78
N
N
I
ILL
—+
+
+
___________
__+ ____—+
_____________
+
I
1
_____
+
___+
$~
N
•
•
I
III
I
LI
__
L~irfi~’
S
____+ _____+
+
N
—
I
•
•
+
+
•
•
N
N
-
•
I
II
N
•
N
I
I
S
•
•
•
•
__
ii’ .zLJI’t
S
•
________
S
-
~
S
_______________________
__________+ __
~i1i
•
II
N
i.e
__
•
—
•
—
—S
•
I
II..
II.
fin.
II
S
:
.
Appendix-i
Biomonitoring 1997 (+=presence,
I
~me
MBERGII
ISA
/ENILE
4GOSETOSA
ISSIMA
I F
Pffshore area
US
A
UMINATA
UVENILE
~CINA
IDA
JS FLExuOSUS
JUVENILE
TURATA
IULATA
HUMILIS
NANA
FORMIS
ENILE
~ACILIS
\URICOMA
(ORENI
!S LONGIMANUS
Species
27128129130131
NEPH HOMB
NEPH INCI
El
-
-
-UN-.-
-
JUVENILE
BERGI
SPEC.
~S ALTAMARINUS
~S ARENARIUS
SPEC.
DIRRIFERA
LLEA KEFERSTEINI
.US SPEC.
~ LONGICORNIS
DORA PULCHRA
~ SIMILIS
‘ENILE
‘ENI
+ NEPHJUVE
NEPH LONG
NERE LONG
NOTO LATE
NIJCU JIJVE
-U
S::::
UUflU..~ -U-
NIJCU TENU
-
+÷
+t
-
+
+
U + +÷+
~
-
-
-
+
~zz~+:
NUCUTURO
OLIG OCHA
OPHE ACUM
OPHE JUVE
-
-
OPHELIMA
OPHI ALBI
OPHI FLEX
OPHI JUVE
OPHI TEXT
ORBI SERT
ORCH HUMI
ORCH NANA
OWEN FUSI
OWEN JUVE
PARA GRAC
PECTAURI
PECT KORE
PERI LONG
PHIL SPEC
JTA
)AE SPEC.
JTA
ITHES
ETUS SERPENS
PEC.
=absence)
Coastal area
S LATERICEUS
S JUVENILE
GIDA
-
--
-t_
-
UUNUUUUN
UUflSNUU
UUNUUUNBU
-
-
•
-
-
-
U.N...
-:i,:~-~.
-
-
-4
-
80
PHOL MINU
PHOR ONID
PHYL LODO
PISI REMO
PLAT HYHE
POEC SERP
POLY DORA
POLY JUVE
POLY KINB
POLY NOID
PONT ALTA
PONT AREN
PRIA PULl
PRIO CIRR
PROT KEFE
PSAM MODR
PSEU LONG
PSEU PULC
PSEU SIMI
RHOD JUVE
RHOD LOVE
SCALIBREG
SCOLOPLO
SCOLELEP
SCOLOPLO
SCOLELEP
SIGALION
SIPHONOE
SIPUNCUUDA
SOSANE GRA
SPHAEROSYL
SPIOPHANES
SPIO FILICOR
SPIOPHANES
SPIOPHANES
SPIONIDAE S
SPISULA ELLI
SPISULA SUB
STENULA RUI
STHENELAIS
STHENELAIS
STREPTOSYL
SYNCHELIDIU
SYNELMIS KL
TELLINA FAB
TELLINA PYG
TEREBELLIDA
TEREBELLIDE
THRACIA CO
THRACIA PHI
THRACIA SPE
THYASIRA FL
TRAVISIA FO
TURBONILLA
UPOGEBIA DL
UROTHOE BR
UROTHOE EL
UROTHOE PC
VENUS STRIA
WESTWOODI
1’
A•1—
I
I
I
I
—I
—
Coastal area
~ n•-1*.
151 Code
,iz,I.zUzL:izIHzLJ..zL.Wzi~LIN~
4+4
4+44+44+
+
+ + 4
÷__________ +
-I
•
SCOLARMI
SCOLBONN
SCOLJUVE
SCOLSOLJA
SIGAMATH
___
I
I,
•
U
U
•1
U
U
-I-I
SIPHKROY
SIPUNCUL
-H
U
+
+
+ +
+
+4+4+44+,
SPHAHYTR
SOSAGRAC
+
+ SPIOBOMB
+4+
SPIOFILI
+J
En
44+4
H ++
-
4
+4
__________
___
4
-
SPIS
ELLI
+
SPIOJUVE
++SP~SSUBT
STENRUBR
STI-IEBOA
STIlE LIMI
STREWEBS
-~
-~
I
nun...
nun
U..
n nnn
•nn a
I I
+
SYNC MACU
SYNEKLAT
+ + _____ +TELLFABU
TELL PYGM
TEREBELL
—
-
I
TERE STRO
THRACONV
-I
I
•:
£
•
I
•
I•
I
•
zJzJ
•I
a
U
us
II
U
III
flU
U
U
-
-
-
-
-
UPOGOELT
UROTBREV
UROTELEG
t~.:~uRoTPosE
- IVENU STRI
WEST CAEC
Appendix 2 Biomonitoring 1997
-
NOTE
Explanation of abbreviations in the tables:
N
B
SUMS
NSPC
SH-W
SIMP
Number of individuals per
Biomass in g AFDW/m2
= Sum of densities per boxcore
= Number of species per boxcore
= Shannon-Wiener index of diversity
= Simpson index of dominance
=
=
All species names have been abbreviated by the first four characters of the generic name
and the first four characters of the specific name. For full scientific names, see Appendix-i.
Station index:
Doa~er Bank
DOG 1-5
DOG 6-7
Oyster Ground
OYS 1-3
OYS 4-8
OYS 9-13
OYS 14-18
OYS 19-23
OYS 24-28
OYS 29-33
0YS34-38
OYS 39-42
-p.
-p.
83
84
-p.
-p.
-p.
-p.
p.
84
85
86
87
-
p.
p.
-p.
p.
-
-
-
89
90
91
92
93
Offshore area
OFF
1
OFF 2-6
OFF 7-11
OFF 12-16
OFF 17-21
OFF 22-26
OFF 27-31
OFF 28-36
-p. 93
-p. 95
p. 96
-p. 97
-p. 98
-p. 99
-p. 100
p. 101
-
-
Coastal area
COA 1- 10
COA 11-15
p. 102
-p. 103
-
Appendix 2 Biomonitoring 1997
-
DOG 1
STATION:
N
CRUSTACEA
ANPEBREV
.0
ATYLFAL.C
0.0
BATF4ELEG
1
.6
BATHGUIL
.0
BATHJUVE
8.5
BATHTENU
.0
CAPRELLI
14.6
DIASBRAD
.0
IPHITRIS
14.6
LEUCINCI
14.6
NEGAAGIL
14.6
RCFIHUNI
.0
PERILONG
4 .9
PONTALTA
.0
PSEULONG
0.0
SIPHKROY
0.0
STENRUBR
0.0
SYNCHACU
29.3
UROTPOSE
117.0
ECHINODERJ4ATA
ACROBRAC
204.8
ECHICORD
0.0
ECHIJUVE
0.0
ECHIPUSI
0.0
OPHIJUVE
58.5
MOLLUSCA
ABRAALBA
0.0
ABRAPRIS
0.0
CULTPELL
0.0
CYLICYLI
14.6
DOSISPEC
0.0
ENSIENSI
0.0
GARIFERV
0.0
MACTCORA
0.0
MONTFERR
0.0
HYSEBIDE
0.0
MYSIUNDA
14.6
NATIALDE
14.6
TEL.LFABU
14.6
VENUSTRI
0.0
PQLYCHA ETA
ARICHINU
29.3
CAPITELL
58.5
CHAESETO
160.9
ETEOJUVE
0.0
ETEOLONG
0.0
GONIMACU
73.2
HARMLUNU
0.0
LANICONC
29.3
MAGEALLE
14.6
MAGEJUVE
175.6
MAGEPAPI
234.1
NEPHCAEC
0.0
NEPHCIRR
43.9
NEPHHOMB
14,6
NEPHJUVE
0.0
NOTOLATE
0.0
OPHELIMA
14.6
OWENFUSI
14.6
PHOLNINU
43.9
POECSERP
14.6
SCALINFL
14.6
SCOLARMI
29.3
SCOLBONN
0.0
$COLSQUA
29.3
SIGAMATH
0.0
SPIOBOMB
14.6
SPIOFILI
73.2
SPIOJUVE
0.0
MISCELLANEOUS
EDWACLAP
0.0
NEMERTIN
58.5
PHORONID
468.2
SUNS
2413.8
DIVERSITY
NSPC
36
SH’W
2.985
SIMP
0.078
DOG 2
DOG 3
0.000
0.000
0.053
0.000
0.012
0.000
0.003
0.000
0.015
0.004
0.004
0.000
0.013
0.000
0.000
0.000
0.000
0.009
0.035
14.6
0.0
87.8
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14,6
14.6
0.0
0.0
0.0
0.0
0.0
0.022
0.000
0.026
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.004
0.004
0.000
0.000
0.000
0.000
0.000
14.6
14,6
336.5
73.2
73.2
0.0
14.6
14.6
14.6
0.0
14.6
0.0
43.9
14.6
0.0
102.4
0.0
0.0
219.5
0.022
0.004
0.101
0.022
0.015
0.000
0.003
0.012
0.015
0.000
0.004
0.000
0.013
0.004
0.000
0.031
0.000
0.000
0.066
14.6
14.6
380.4
43.9
0.0
29.3
0.0
14.6
0.0
0.0
0.0
0.0
14.6
0.0
0,0
73.2
0.0
0.0
87.8
0.022
0.004
0.114
0.013
0.000
0.009
0.000
0.022
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0.022
0.000
0.000
0.026
14.6
0.0
43.9
29.3
29.3
0.0
0.0
14.6
29.3
0.0
0.0
29.3
73.2
0.0
43.9
0.0
43.9
0.0
29.3
0.007
0.000
0.013
0,009
0.006
0.000
0.000
0,007
0.029
0.000
0.000
0.009
0.022
0.000
0.009
0.000
0.013
0.000
0.009
0.737
0.000
0.000
0.000
0.012
43.9
0.0
0.0
0.0
29.3
5.452
0.000
0.000
0.000
0.006
146.3
0.0
14.6
14.6
43.9
2.134
0.000
0.002
0.016
0.009
0.0
0.0
0.0
29.3
131.7
0.000
0.000
0.000
0.363
0.026
43.9
14.6
0.0
0.0
87.8
2.562
1.467
0.000
0.000
0.018
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.003
0.038
0.002
0.000
0.0
0.0
29.3
0.0
0.0
14.6
0.0
14.6
14.6
131.7
0.0
14.6
190.2
14.6
0.000
0.000
0.005
0.000
0,000
3.640
0.000
0.001
0.005
0.042
0.000
0.003
0.108
0.001
0.0
0.0
14.6
0.0
43.9
0.0
14.6
0.0
0.0
146.3
0.0
43.9
87.8
0.0
0.000
0.000
0.069
0.000
0.084
0.000
0.037
0.000
0.000
0.030
0.000
0.094
0.152
0.000
29.3
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
14.6
29.3
14.6
0.006
0.000
0.000
0.000
0.000
0.000
0.000
0.001
0.000
0.000
0.000
0.020
0.026
0.002
0.0
29.3
14.6
0.0
0.0
14.6
0.0
29.3
29.3
87.8
0.0
58.5
102.4
0.0
0.000
0.007
0.002
0.000
0.000
1.097
0.000
0.003
0.022
0.026
0.000
0.085
0.246
0.000
0.006
0.008
0.029
0.000
0.000
0.203
0.000
0.263
0.083
0.023
0.328
0.000
0.322
0.585
0.000
0.000
0.066
0.004
0.006
0.014
0.315
0.014
0.000
0.050
0.000
0.008
0.006
0.000
0.0
14.6
43.9
0.0
0.0
43.9
29.3
0.0
0.0
117.0
409.6
0.0
0,0
14.6
14.6
0.0
0.0
0.0
0.0
14.6
0.0
14.6
0.0
0.0
14.6
0.0
131.7
87.8
0.000
0.002
0.014
0.000
0.000
0.025
0.010
0.000
0.000
0.006
0.110
0.000
0.000
0.035
0.004
0.000
0.000
0.000
0.000
0.004
0.000
0.015
0.000
0.000
0.355
0.000
0.017
0.006
87.8
0.0
73.2
0.0
14.6
43.9
0.0
14.6
0.0
190.2
43.9
0.0
14.6
14.6
0.0
0.0
0.0
43.9
73.2
14.6
0.0
14.6
29.3
0.0
0.0
73.2
29.3
0.0
0.004
0.000
0.006
0.000
0.002
0.014
0.000
0.046
0.000
0.006
0.019
0.000
0.014
0.274
0.000
0.000
0.000
0.008
0.004
0.002
0.000
0.004
0.348
0.000
0.000
0.027
0.014
0.000
0.0
0.0
0.0
0.0
14.6
29.3
14.6
0.0
0.0
87.8
146.3
0.0
131.7
73.2
0.0
175.6
0.0
29.3
131.7
14.6
14.6
14.6
0.0
0.0
0.0
117.0
87.8
29.3
0.000
0.000
0.000
0.000
0.004
0.110
0.023
0.000
0.000
0.014
0.137
0.000
0.187
0.620
0.000
0.850
0.000
0.114
0.008
0.021
0.043
0.008
0.000
0,000
0.000
0.054
0.031
0.003
0.0
0.0
14.6
14,6
0.0
29.3
0.0
0.0
0.0
278.0
570.6
14.6
0.0
0.0
0.0
0.0
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
29.3
58.5
263.3
409.6
0.000
0.000
0.002
0.002
0.000
0.019
0.000
0.000
0.000
0.017
0.220
1.545
0.000
0.000
0.000
0,000
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.000
0.043
0.093
0.058
0.019
0.000
0.0
0.042
43.9
0.056
14.6
3.005 2662.9
0.000
0.023
0.001
7.714
29
2.729
0.106
42
3.271
0.054
N
0.106
0.0
0.541
29.3
0.015
58.5
4.390 2136.2
34
3.053
0.068
B
N
5
B
0.000
14.6
0.006
73.2
0.000
29.3
9.932 2414.0
B
DOG
N
0.000
0.0
0.064
29.3
0.251
0.0
3.587 1623.7
N
DOG 4
B
35
2.841
0.098
B
Appendix 2 Biomonitoring 1997
-
DOG 6
3TATION:
N
:RUSTACBA
AMPEBREV
ANPETENU
ATYLFALC
BATHELEG
BATHGUIL
BATHJIJVE
CALLSUBT
COROPHITJ
DIASBRAD
DIASL.AEV
EU000EPO
HARPANTE
IPHITRIS
HEGAAGIL
ORCHNANA
PERILONG
PONTALTA
SIPHKROY
UROTPOSE
DOG 7
B
N
OYS 1
B
N
OYS 2
OYS 3
B
N
B
N
B
0.0
0.0
14.6
263.3
0.0
29.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
14.6
29.3
0.000
0.000
0.004
0.079
0.000
0.086
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0.004
0.004
0.009
14.6
0.015
14.6
0.053
0.0
0.000
0.0
0.000
0.0
14.6
87.8
146.3
43.9
0.0
0.0
14.6
0.0
0.0
0.0
58.5
43.9
14.6
29.3
0.0
58.5
307.2
0.000
0.004
0.026
0.044
0.009
0.000
0.000
0.015
0.000
0.000
0.000
0.024
0.013
0.004
0.009
0,000
0.018
0.092
0.0
0.0
0.0
0.0
0.0
9.3
0.0
3.2
0.0
0.0
0.0
0.0
0.0
0.0
43.9
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.116
0.000
0,035
0.000
0.000
0.000
0.000
0.000
0.000
0.013
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0,000
0.000
0.000
0.821
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
43.9
0.0
14.6
0.0
0.0
0.0
14.6
0.0
14.6
14.6
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.013
0.000
0.004
0.000
0.000
0.000
0.003
0.000
0.007
0.003
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.000
14.6
0.0
0.0
14.6
14.6
0.0
29.3
0.0
0.092
0.000
0.000
0.056
0.009
0.000
0.023
0.000
29.3
0.0
0.0
0.0
0.0
14.6
0.0
14.6
0.782
0.000
0.000
0.000
0,000
0.002
0.000
0.003
0.0
951.0
14.6
0.0
14.6
0.0
0.0
0.0
0.000
2.644
0.021
0.000
3.010
0.000
0.000
0.000
0.0
0.0
0.0
0.0
14,6
0.0
0.0
0.0
0.000
0.000
0.000
0.000
1.109
0.000
0.000
0.000
0.0
219.5
0.0
0.0
0.0
29.3
0.0
512.1
0.000
1.913
0.000
0.000
0.000
0.003
0.000
0.154
ABRAALBA
0.0
ABRAPRIS
ACANECHI
APLACOPH
ARCTISLA
CINGVITR
CORBGIBB
CULTPELL
CYLICYLI
DOSILUPI
ENSIENSI
ENSISPEC
GASTROPO
HONTFERR
MONTSPEC
NYSEBIDE
NATIALDE
NUCUTENU
NUCUTURG
TELLFABU
THYAFLEX
VENUSTRI
‘OLYCHAETA
ARICMINU
CAPITELL
CHAESETO
DIPLGLAU
ETEOLONG
EUHISANG
GLYCNORD
GLYCR0TJX
GONIMACU
GONISPEC
LANICONC
MAGEJTJVE
MAGEPAPI
MEDIFRAG
NEPHCAEC
NEPHCIRR
NEPHHOMB
NEPHJUVE
NERELONG
NOTOLATE
OPHEACUM
OPHELIMA
OPHIFLEX
OWENFUSI
PARAGRAC
PECTAURI
PECTKORE
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
14.6
0.0
0.0
29.3
29.3
0.0
0.0
0.0
0.0
0.0
0,000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1.554
0.000
0.003
0.000
0.000
0.009
0.071
0.000
0.000
0.000
0.000
0.000
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
43.9
0.0
14.6
0.0
0.0
0.0
58.5
87.8
0.0
0.0
29.3
0.0
0.0
0.000
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.004
0.000
2.872
0.000
0.000
0.000
0.018
0.196
0.000
0.000
0.050
0.000
0.000
14.6
0.0
0.0
0.0
0.0
14.6
0.0
0.0
219.5
0.0
0.0
0.0
0.0
0.0
43.9
234.1
0.0
0.0
0.0
0.0
43.9
0.0
0.002
0.000
0.000
0.000
0.000
0.003
0.000
0.000
0.160
0.000
0.000
0.000
0.000
0.000
0.009
0.047
0.000
0,000
0.000
0.000
0.004
0.000
0.0
0.0
0.0
0.0
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
102.4
0.0
14.6
0.0
0.0
29.3
0.000
0.000
0.000
0.000
0.000
0.000
0.005
0.000
0.000
0.000
0.000
0.000
0.000
0.026
0.000
0.000
0.036
0.000
0.128
0.000
0.000
0.000
0.0
0.0
29.3
29.3
14.6
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
117.0
0.0
14.6
0.0
0.0
0.0
0.0
0.000
0.000
0.009
0.022
0,005
0.000
0.000
0.001
0.000
0,000
0.000
0.000
0.000
0.000
0,000
0.023
0.000
0.052
0.000
0.000
0.000
0.000
29.3
0.0
0.0
0.0
43.9
29.3
0.0
0.0
43.9
0.0
29.3
29.3
307.2
0.0
0.0
117.0
0.0
73.2
0.0
0.0
0.0
29.3
0.0
512.1
0.0
0.0
0.0
0.004
0.000
0.000
0.000
0.012
0.006
0,000
0.000
0.062
0,000
0.087
0.002
0.185
0.000
0.000
0.352
0.000
0.008
0,000
0.000
0.000
0.023
0.000
0.197
0.000
0.000
0.000
0.0
0.0
0.0
0.0
29.3
0.0
0.0
14.6
14.6
14.6
0.0
43.9
278.0
0.0
14.6
B7.8
73.2
14.6
0.0
73.2
0.0
0.0
0.0
336.5
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0.019
0.006
0.001
0.000
0.002
0.098
0.000
0.823
0.075
0.089
0.004
0.000
0.925
0.000
0.000
0.000
0,174
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
9.3
0.0
0 0
6
0 0
0 0
0.000
0.000
0.000
0.000
0.000
0.000
0.037
0.000
0.000
0.000
0.000
0.000
0,000
0.002
0.000
0.000
0.363
0.000
0.000
0.745
0.000
0.000
0.004
0,000
0.000
0.197
0.000
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
43.9
0.0
0.0
0.0
29.3
0.0
29.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0,000
0.000
0.000
0.021
0,000
0.000
0.000
0.037
0.000
0,000
0.000
0.531
0.000
0.087
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.0
29.3
29.3
29.3
0.0
0.0
0.0
0,0
29.3
0.0
0.0
73.2
0.0
0.0
0.0
0.0
14.6
29.3
0.0
0.0
14,6
0.0
0.0
0.0
14.6
0.0
29.3
0.000
0.015
0.010
0.008
0.000
0.000
0.000
0.000
0.0GB
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.149
0.006
0.000
0.000
0.533
0.000
0.000
0.000
0.004
0.000
0.174
CHINODERMATA
ACROBRAC
ANPHFILI
ASTEJUVE
ASTRIRRE
ECHICORD
ECHIJUVE
ECHIPUSI
OPHIJUVE
(OLLUSCA
0 0
0 0
1
6
0 0
0.0
29 3
0.0
Appendix 2 Biomonitoring 1997
-
PHOLMINU
0.0
POECSERP
0.0
PRIOCIRR
0.0
SCALINFL
0.0
SCOLARMI
0.0
SCOLBONN
0.0
SCOLSQUA
14.6
SIGAMATH
43.9
SPIOBOMB 219.5
SPIOFILI
58.5
STHEBOA
0.0
MISCELLANEOUS
ANTHOZOA
0.0
GOLFELON
0.0
NEMERTIN
43.9
PHORONID 438.9
PLATFIYHE
0.0
PRIAPULI
0.0
SUMS
2604.3
DIVERSITY
NSPC
32
SH’W
2.708
SIMP
0.104
STATION:
OYS
0.000
0.000
0.000
0.000
0 000
0.000
0.039
0.006
0.178
0.060
0.000
0.0
0.0
0.0
0.0
0.0
14.6
0.0
146.3
117.0
0.0
43.9
0.000
14.6
0.000
0.0
0.048
29.3
0.048 278.0
0.000
0.0.
0.000
0.0
3.242 2779.6
0.000
0.000
0.000
0.000
0.000
0.102
0.000
0.097
0.062
0.000
0.014
117.0
0.021
0.0
0.0
14.6
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.004
0.093
0.000
0.000
0,000
0.000
0.000
0.000
0.000
14.6
0.0
0.0
14.6
14.6
0.0
0.0
14.6
14.6
0.0
0.003
29.3
0.000
14.6
0.016
73.2
0.019 219.5
0.000
14.6
0.000
0.0
6.737 2326.2
0.019
0.004
0.708
0.029
0.019
0.000
8.362
0.0
0.0
0.0
14.6
0.0
0.0
424.1
40
3.147
0.062
4
N
OYS
N
B
27
2.269
0.201
S
B
0Th
N
0.000
0.002
0.000
0 000
0.021
0.021
0.000
0.000
0.002
0.002
0.000
131.7
0.0
0.0
14.6
497.4
0.0
0.0
0.0
14.6
0.0
0.0
0.023
0.000
0.000
0.039
0.825
0.000
0.000
0.000
0.004
0.000
0.000
0.000
29.3
0.000
0.0
0.000
14.6
0.002
29.3
0.000
0.0
0.000
14.6
2.852 2136.1
2.298
0.000
0.013
0.019
0.000
0.029
6,376
17
2.592
0.099
6
33
2.600
0.133
OYS 7
B
N
0Th
B
N
8
B
CRUSTACEA
AMPEMACR
0.0
0.0
0.000
0.0
0.000
29.3
0.029
0.0
0,000
ATYLSWAM
0.0
0.000
0.0
0.000
0.0
0.000
14.6
0.004
0.0
0.000
BATHGUIL
14.6
BATHTENU
58.5
CALLOUS’]’
0.0
CAMPGLAB
0.0
COROAFFI
0,0
CORYCASS
14.6
DIASBRAD
0.0
EUDODEFO
0.0
EUDOEt4AR
0.0
EUDOTRUN
0.0
HARPANTE
0.0
HIPPDENT
0.0
ORCHNANA
0.0
PERILONG
58.5
PSEUL,ONG
29.3
ECHINODERMATA
ACROBRAC
73.2
AMPHFILI
14.6
ASTATRIA
14.6
ECHICORD
0.0
ECHIJUVE
0.0
0PHIALBI
0.0
OPHIJUVE
190.2
140 LLUSCA
ABRAALBA
29.3
APLACOPH
0.0
ARCTISLA
29.3
CINGVITR
0.0
C0RBGIBB
0.0
CULTPELL
73.2
CYLICYLI
0.0
ENSIENSI
14.6
EULIAL8A
0.0
GASTROPO
0.0
LEPTSQUA
0.0
MYSEBIDE
175,6
NATIALDE
43.9
NUCUTENU
0.0
NUCUTURG
43.9
SPISSUST
0.0
TELLFABU
73.2
THRAPHAS
29.3
THYAFLEX
117.0
VENUSTRI
73.2
0.004
0.018
0.000
0.000
0.000
9.722
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0,018
0.006
0.000
0.0
0.0
43.9
0.0
0.0
0.0
0.0
0.0
0.0
0.0
73.2
0.0
14.6
0.0
0.0
0.000
0.000
0.430
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.022
0.000
0.004
0.000
0.000
0.0
0.0
0.0
0.0
14.6
0.0
0,0
14.6
0.0
0.0
0.0
14.6
0.0
0.0
0,0
0.000
0.000
0.000
0.000
0.003
0.000
0.000
0.003
0.000
0.000
0,000
0.004
0.000
0.000
0.000
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
131.7
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.003
0.000
0.000
0.000
0.000
0.026
0.000
0,000
0.000
0.000
0.000
0.000
0.0
0.0
29.3
0.0
0.0
0.0
29.3
0.0
0.0
29.3
0.0
0,0
0.0
0.0
0.0
0.000
0.000
2.278
0.000
0.000
0.000
0.015
0.000
0.000
0.006
0.000
0.000
0.000
0.000
0.000
4.881
0.053
0.001
0.000
0.000
0.000
0.038
0.0
351.1
0.0
43.9
0.0
29.3
951.0
0.000
0.928
0.000
0.059
0.000
0.014
0.190
0.0
687.6
0.0
0.0
14.6
0.0
0.0
0.000
0.0
8.262
468.2
0.000
0.0
0.000
0.0
0.002
14.6
0.000
0.0
0.000 1243.6
0.000
1.294
0.000
0.000
0.002
0.000
0.249
0.0
0.0
0.0
14,6
0.0
117.0
424.3
0.000
0.000
0.000
0.028
0.000
2.140
0.085
0.002
0.000
0.002
0.000
0,000
0.476
0.000
1.170
0.000
0.000
0.000
0.035
0.004
0.000
0.342
0.000
0.082
0.004
0.283
1.636
0.0
0.0
0.0
365.8
58.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
73.2
0.0
0.0
0.0
43.9
0.000
0.000
0.000
0.044
0.307
0.000
0.000
0.000
0.000
0.000
0,000
0.000
0.011
0.000
0.000
0.023
0.000
0.000
0.000
0.002
43.9
0.0
14.6
0.0
0.0
0.0
58.5
0.0
43.9
0.0
0.0
102.4
0.0
73.2
0.0
0.0
14.6
0.0
0.0
0.0
0.003
0.000
0.014
0.000
0.000
0.000
0.039
0.000
0.004
0,000
0.000
0.021
0.000
0.051
0.000
0.000
0.001
0,000
0.000
0.000
0.0
58.5
102.4
29.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0
73.2
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.073
0.045
0.006
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.015
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
14.6
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
29.3
0.0
87.8
0.0
146.3
0.0
0.0
0.0
0.0
0.0
0.575
0.000
0.000
0.000
0.000
0.000
0.101
0.000
0.000
0.007
0.029
0.000
0.085
0.000
0.794
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.015
0.000
0.000
29.3
0.0
0.0
0.0
14.6
0.0
0.012
0.000
0.000
0.000
4.200
0.000
.000
0.0
73.2
0.0
0.0
0.0
0.0
14.6
0.000
0.019
0.000
0.000
0.000
0.000
0.006
0.0
0.0
14.6
58.5
0,0
29.3
14.6
0.000
0.000
0.002
0.014
0.000
0.102
0.004
0.0
0.0
0.0
0,0
0.0
0,0
0.0
0.000
0.000
0.000
0.000
0 000
0 000
0.000
POLYCHARTA
ANAIJUVE
APHRACUL
APHRJUVE
CHAESETO
CHAEVARI
DIPLGLAU
ETEOLONG
0.0
0.0
0.0
73.2
0.0
0.0
0.
.
.
Appendix 2 Biomonitoring 1997
-
EUMISANG
14.6
0.004
0.0
GATTCIRR
0.0
0.000
14.6
GLYCNORD
43.9
0.039
0.0
GLYCR0UX
0.0
0.000
43.9
G0NIMACU
0.0
0.000
29.3
GYPTCAPE
0.0
0.000
14.6
HARMJUVE
14.6
0.010
0.0
HARMLUNU
0.0
0.000
0.0
LUMBLATR
0.0
0.00.P
87.8
LYSILOVE
0.0
0.000
0.0
MAGEALLE
43.9
0.460
0.0
MAGEPAPI
907.1
0.404
0.0
MALDANID
14.6
0.149
0.0
MEDIFRAG
0.0
0.000
0.0
NEPHHOMB
43.9
1.027
29.3
NEPHINCI
0.0
0.000
14.6
NEPHJUVE
0.0
0.000
14.6
NERELONG
0.0
0.000
14.6
NOTOLATE
0.0
0.000
29.3
OPHEACUM
0.0
0.000
0.0
OPF{IFLEX
0.0
0.000
0.0
ORBISERT
0.0
0.000
14.6
QWENFTJSI
0.0
0.000
14.6
OWENJUVE
0.0
0.000
0.0
PARAGRAC
0.0
0.000
14.6
PECTAURI
0.0
0.000
0.0
PECTKORE
0.0
0.000
0.0
PHOLMINU
58.5
0.010
131.7
POECSERP
0.0
0.000
43.9
POLYDORA
0.0
0.000
29.3
RHODJUVE
0.0
0.000
0.0
RHODLOVE
0.0
0.000
0.0
SCAL.INFL
0.0
0.000
0.0
SCOLARMI
14.6
0.010
0.0
SIGAMATH
14.6
0.185
0.0
SPIOBOMB
790.0
0.193
131.7
SPIOFILI
29.3
0.012
0.0
SPIOJUVE
0.0
0.000
0.0
SPIOKROE
0.0
0.000
0.0
STHELIMI
0.0
0.000
0.0
SYNEKLAT
0.0
0.000
14.6
TERESTRO
0.0
0.000
14.6
MISCELLAN~Q2g
ANTHOZOA
0.0
0.000
0.0
EDWACLAP
0.0
0.000
0.0
GOLFELON
0.0
0.000
14.6
NEMERTIN
117.0
0.058
73.2
PHORONID
131.7
0.017
131.7
PLATHYHE
0.00.000
0.0
SUMS
3482.1
21.379 3028.6
DIVERSIT!
NSPC
35
36
SH’W
2.666
2.663
SIMP
0.133
0.137
STATION:
QYS
N
CRUSTACEA
AMPEBREV
0.0
AMPHIPOD
0.0
BATHELEG
131.7
CALL2UVE
0.0
CALLSUBT
43.9
CAPRELLI
0.0
CIROCRAN
0.0
ETJDODEFO
29.3
EUDOTRUN
0.0
HARPANTE
14.6
HARPCREN
0.0
HIPPDENT
0.0
LEUCINCI
0.0
LEUCLILL
29.3
ORCHNANA
14.6
PERILONG
0.0
UPOGDELT
0.0
ECHINODEPJ4ATA
AMPHFILI
117.0
8RISLYRI
0.0
ECHICORD
0.0
ECHIPUSI
160.9
OPHIAL8I
0.0
9
B
QYS
N
0.000
0.743
0.000
1.099
0.023
0.006
0.000
0.000
0.187
0.000
0.000
0.000
0.000
0.000
0.058
0.340
0.006
0.006
0.435
0.000
0.000
0.043
0.004
0.000
0.001
0.000
0.000
0.039
0.025
0.027
0.000
0.000
0.000
0.000
0.000
0.017
0.000
0.000
0.000
0.000
0.010
1.172
0.0
0.0
0.0
0.0
43.9
0.0
0.0
0.0
0.0
0.0
0.0
73.2
0.0
0.0
102.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
43.9
0.0
0.0
0.0
585.2
43.9
0.0
0.0
0.0
0.0
160.9
0.0
29.3
43.9
102,4
0.0
0.0
0.0
0.0
0.000
14.6
0.000
0.0
0.008
0.0
0.354
29.3
0.012
73.2
0.000
0.0
10.859 2531.0
0.000
0.000
0.000
0.000
0.010
0.000
0.000
0.000
0.000
0.000
0.000
0.019
0.000
0.000
1.759
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.010
0.000
0.000
0.000
0.106
0.085
0.000
0.000
0.000
0.000
0.635
0.000
0.029
0.010
0.023
0.000
0.000
0.000
0.000
0.061
0.0
0.000
73.2
0.000
0.0
0.003
14.6
0.010
190.2
0.000
0.0
11.192 3160.1
27
2.517
0.142
10
B
OYS
N
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
43.9
0.0
0.0
0.0
43.9
29.3
14.6
0.0
0.0
0.0
43.9
14.6
14.6
204.8
0.0
0.0
14.6
29.3
87.8
0.0
0.0
0.0
0.0
0.0
14.6
14.6
0.0
0.0
0.000
0.000
0.000
0,000
0.000
0.000
0.000
0,000
0.000
0.010
0.000
0.000
0.000
0.000
0.703
0.000
0.000
0.000
0.572
0.460
0.054
0.000
0.000
0.000
0.004
0.266
0.398
0.043
0.000
0.000
0.002
0.566
0.688
0,000
0.000
0.000
0.000
0.000
0.019
0.010
0.000
0.000
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
14.6
0.0
0.0
0.0
0.0
234.1
58.5
0.0
0.0
14.6
0.0
0.0
0.0
0,0
0.0
0.0
0.0
0.0
0.0
0.0
73.2
29.3
0.0
0.0
0.0
14.6
0.0
204.8
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.077
0.000
0.000
0.010
0.043
0.000
0.000
0.000
0.000
0.068
1.168
0.000
0.000
0.023
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.019
0.010
0.000
0.000
0.000
0.006
0.000
0.039
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.0
0.341
0.0
0.000
0.0
0.032
43.9
0.048
833.9
0.000
14.6
6.082 2516.3
0.000
0.000
0.000
10.663
0.116
0.006
18.390
32
2.380
0.191
11
8
QYS
N
0.000
0.000
0.040
0.000
0.088
0.000
0.000
0.006
0.000
0.004
0.000
0.000
0.000
0.009
0.004
0.000
0.000
0.0
0.0
0.0
0.0
14.6
0.0
0.0
29.3
14.6
14.6
0,0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
1.747
0.000
0.000
0.006
0.003
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.0
0.0
0.0
0.0
43.9
14.6
0.0
0.0
58.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
1.119
0.003
0.000
0.000
0.012
0.000
0.000
0,000
0.000
0.000
0.000
0.000
0.000
0.0
14.6
0.0
73.2
73.2
0.0
14.6
0.0
29.3
146.3
14.6
14.6
14.6
0.0
14.6
0.0
43.9
0.113
0.000
0.000
0.030
0.000
892.4
14.6
14.6
0.0
0.0
7.212
7.599
4.503
0.000
0.000
58.5
0.0
43.9
0.0
117.0
0.041
0.000
0.075
0.000
1.851
190.2
0.0
0.0
0.0
0.0
25
2.335
0.163
12
B
0.000
0.003
0.000
0.130
1.727
0.000
1.224
0.000
0.006
0.044
0.004
0.004
0.004
0.000
0.004
0.000
12.772
QYS
N
13
8
14,6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
0.0
43.9
0.0
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.006
0.000
0.000
0.000
0.000
0.000
0,000
0.013
0.000
0.215 1199.7
0.000
0.0
0.000
29.3
0.000
0.0
0.000
14.6
11.325
0.000
7.218
0.000
0.656
Appendix 2 Biomonitoring 1997
-
OPI4IJUVE
14.6
ABRAALBA
14.6
ABRAPRIS
0.0
ACANECHI
0.0
APLACOPH
0.0
ARCTISLA
0.0
CINGVITR
0.0
CORBGIBB
0.0
CULTPELL
0.0
CYLICYLI
0.0
EULIAL8A
0.0
GASTROPO
0,0
MONTFERR
0.0
MYSEBIDE
0.0
MYSITJNDA
0.0
NATIALDE
14.6
NUCUTENTJ
0.0
NUCUTURG
43.9
TELLFABU
14.6
THYAFLEX
0.0
POLYCHAETA
ANAIMACU
0.0
APHRACUL
0.0
APHRJUVE
0.0
CHAESETO
0.0
CHAEVARI
0.0
DIPLGLAU
0.0
GATTCIRR
0.0
GONIMACU
0.0
GYPTCAPE
0.0
HARMLONG
0.0
LUMBLATR
0.0
MAGEALLE
29.3
MAGEJUVE
87.8
MAGEPAPI
204.8
MEDIFRAG
0.0
NEPHHOMB
14.6
NEPHINCI
0.0
NEPHJUVE
0.0
NOTOLATE
0.0
OPHIFLEX
14.6
ORBISERT
0.0
OWENFUSI
0.0
OWENJUVE
0.0
PECTAURI
0.0
PECTKORE
0.0
PHOLMINU
0.0
POECSERP
29.3
POLYKINB
0.0
PRIOCIRR
0.0
SCOLARMI
14.6
SCOL8ONN
14.6
SIGAMATH
14.6
SPIOBOMB
497.4
SPIOFILI
0.0
SYNEKLAT
0.0
MISCELlANEOUS
ANTHOZOA
0.0
GOLFELON
0.0
GOLFVULG
0.0
NEMERTIN
73.2
PHORONID
73.2
PLATHYHE
0.0
SUNS
1711.6
DIVERSITY
NSPC
25
SH’W
2.552
SIMP
0.127
STATION
N
0.003
994.8
0.199
424.3
0.085
0.0
0.000
965.6
0.193
0.001
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.002
0.000
0.463
0.000
0.000
0.0
14.6
14.6
14.6
0.0
0.0
0.0
14.6
29.3
0.0
0.0
0.0
117.0
14.6
0.0
43.9
0.0
0.0
0.0
0.000
0.128
0.002
0.015
0.000
0.000
0.000
0.099
0.042
0.000
0.000
0.000
0.023
0.007
0.000
0.043
0.000
0.000
0.000
14.6
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
0.0
29.3
0.0
43.9
0.0
58.5
0.0
0.0
0.0
0.0
0.005
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0.044
0.000
0.006
0.000
0.009
0.000
0.017
0.000
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
43.9
29.3
0.0
43.9
0.0
0.0
0.0
0,0
0.0
0.0
29.3
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.009
0.012
0.000
0.020
0.000
0.000
0.000
0.000
0.000
0.000
0.009
0.000
0.000
0.000
29.3
0.0
0,0
0.0
14.6
0.0
0.0
0.0
73.2
14.6
0.0
29.3
204.8
0.0
14.6
58.5
0.0
0.0
14.6
0.006
0.000
0.000
0.000
0.005
0.000
0.000
0.000
0.041
0.002
0.000
0.056
0.041
0.000
0.014
0.069
0.000
0.000
0.065
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.098
0.012
0.261
0.000
1.966
0.000
0.000
0.000
0.035
0.000
0.000
0.000
0.000
0.000
0.000
0.015
0.000
0.000
0.010
0.243
0.550
0.197
0.000
0.000
0.0
14.6
0.0
0.0
14.6
0.0
14.6
14.6
0.0
0.0
0.0
0.0
29.3
0.0
0.0
14.6
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
219.5
0.0
14.6
0.0
58.5
0.0
0.0
0.0
29.3
29.3
0.000
0.004
0.000
0.000
5.929
0.000
0.274
0.006
0.000
0.000
0.000
0.000
0.008
0.000
0.000
0.044
0.000
0.000
2.024
0.000
0.000
0.000
0.000
0.000
0.000
0.039
0.000
0.012
0.000
0.031
0.000
0.000
0.000
0.010
0.008
0.0
0.0
0.0
0.0
0.0
0,0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
29.3
14.6
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
43.9
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0,000
0.000
0.000
0.000
0.000
0.000
0.015
0.000
0.118
0.001
0.000
0.581
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.008
0.000
0.000
0.0
0.0
14.6
14.6
14.6
0.0
43.9
29.3
14.6
0.0
14.6
0.0
0.0
0.0
14.6
14.6
29.3
14.6
43.9
14.6
0.0
0.0
0.0
43.9
14.6
14.6
14.6
0.0
14.6
0.0
0.0
0.0
29.3
0.0
14.6
0.000
0.000
0.002
0.050
2.012
0.000
0.576
0.008
0.027
0.000
0.041
0.000
0.000
0.000
0.002
0.266
0.050
0.002
1.728
0.046
0.000
0,000
0.000
0.012
0.255
0.004
0.004
0.000
0.004
0.000
0.000
0.000
0.004
0.000
0.004
14.6
0,0
0.0
14.6
0.0
14.6
0.0
0.0
0.0
14.6
0.0
0.0
0.0
29.3
0.0
43.9
0.0
0.0
14.6
0.0
14.6
0.0
0.0
0.0
0.0
175.6
0.0
0.0
0.0
58.5
0.0
14.6
29.3
0.0
0.0
0.006
0.000
0.000
0.002
0.000
0.008
0.000
0.000
0.000
0.010
0.000
0.000
0.000
0.008
0.000
0.037
0.000
0.000
0.072
0.000
0.023
0.000
0.000
0.000
0.000
0.023
0.000
0.000
0.000
0.066
0.000
0.021
0.002
0.000
0,000
0.061
0.0
1,949
0.0
0.000
0.0
0.000
14.6
0.019
0.0
0.013
0.0
23.326 3203.9
0.000
0.000
0.000
0.097
0.000
0.000
20.085
0.000
29.3
0.000
0.0
0.000
0.0
0.216
0.0
0.008
219.5
0,000
0.0
4.373 2969.6
0.290
0.0
0.000
0.0
0.000
14.6
0.000
29.3
0.048
263.3
0.000
0.0
30.357 1360.4
30
2.097
0.216
OYS 14
8
0.000
14.6
0.000
87.8
0.006
0.0
0.039
0.0
0.068
146.3
0.000
29.3
4.106 1492.1
21
2.379
0.154
OYS 15
N
B
40
3.294
0.053
QYS 16
N
B
29
2.016
0.240
OYS 17
N
8
OYS 18
N
8
CRUSflCEA
AMPEBREV
AMPETENU
6ATHELEG
BATHJTJVE
6ATHTENU
CALLJUVE
CALLSU8T
EU000EFO
0.0
0.0
0.0
14.6
0.0
0.0
14.6
0.0
0.000
0.000
0.000
0.003
0.000
0.000
0.393
0.000
0.0
14.6
0.0
0.0
0.0
0.0
14.6
0.0
0.000
0.004
0,000
0.000
0.000
0.000
0.154
0.000
14.6
0.0
14.6
0.0
0.0
0.0
73.2
0.0
0.004
0.000
0.004
0.000
0.000
0.000
3.081
0.000
29.3
0.0
0.0
0.0
14.6
0.0
43.9
58.5
0.110
0.000
0.000
0.000
0.004
0.000
0.779
0.012
0.0
0.0
14.6
0.0
0.0
43.9
0.0
0.0
0.000
0.000
0.004
0.000
0.000
0.026
0.000
0.000
Appendix -2 Biomonitoring 1997
EUDOEMAR
0.0
EUDOTRUN
0.0
HARPANTE
0.0
HARPPECT
14.6
HIPPOENT
0.0
ORCHNANA
0.0
PERILONG
0.0
UROTELEG
0.0
ECHIN0DE~4ATA
AMPHFILI
29.3
ECHIFLAV
0.0
ECHIJUVE
0.0
ECHIPUSI
0.0
OPHIJUVE
0.0
MOLLUSCA
ABRAAL8A
0.0
ARCTISLA
0.0
CINGVITR
102.4
COR8GIBB
43.9
CULTPELL
0.0
CYLICYL.I
0.0
DOSILUPI
0.0
EULIAL8A
0.0
GASTROPO
0.0
MONTFERR
0.0
MYSE8IDE
0.0
NATIALDE
0.0
NUCUTURG
0.0
TELLFA8U
0.0
THRAPHAS
0.0
VENUSTRI
14.6
?OLYCHAETA
ANAIJUVE
0.0
CHAEJUVE
0.0
CHAESETO
0.0
CHAEVARI
43.9
CHONSPEC
0.0
DIPLGLAU
0.0
ETEOLONG
0.0
ETJMISANG
0.0
EXOGHE8E
14.6
GA’fl’CIRR
43.9
GLYCROUX
29.3
GONIMACU
0.0
GYPTCAPE
0.0
HARMLONG
0.0
LYSILOVE
0.0
MAGEJUVE
14.6
MAGEPAPI
0.0
NEPHHOM8
0.0
NEPHINCI
14.6
NERELONG
14.6
NOTOLATE
43.9
OPHIFLEX
0.0
PARAGRAC
73.2
PECTAURI
0.0
PHOLMINU
0.0
POECSERP
14.6
SCALINFL
0.0
SCOLARMI
0.0
SCOLBONN
0.0
SF1080848
0.0
SPIOFILI
0.0
STHELIMI
0.0
SYNEKLAT
73.2
MISCELLANEOUS
ANTHOZOA
0.0
GOLFELON
73.2
HYDROZOA
14.6
NEMERTIN
0.0
PHORONID
73.2
PLATHYHE
.0
SUMS
775.4
PiV~gS1TY
NSPC
21
SHW
2.804
SIMP
0.071
0.000
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.0
67.8
29.3
0.0
0.0
0.0
0.0
0.0
0.000
0.018
0.009
0.000
0.000
0.000
0.000
0.000
14.6
43.9
43.9
0.0
0.0
0.0
0.0
0.0
0.003
0.009
0.013
0.000
0.000
0.000
0.000
0.000
0.0
0.0
29.3
0.0
14.6
14.6
0.0
14.6
0.000
0.000
0.009
0.000
0.004
0.004
0.000
0.004
0.0
0.0
14.6
0.0
0.0
0.0
14.6
0.0
0 000
0.000
0.004
0 000
0.000
0.000
0.004
0.000
0.133
0.000
0.000
0.000
0.000
87.8
0.0
14.6
0.0
117.0
0.246
0.000
0.002
0.000
0.023
87.8
14.6
0.0
0.0
43.9
1.606
0.014
0.000
0.000
0.009
175.6
0.0
0.0
0.0
263.3
1.229
0.000
0.000
0.000
0.047
0.0
0.0
0.0
146.3
146.3
0.000
0.000
0.000
0.020
0.029
0.000
0.000
0.021
0.102
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.002
58.5
0.0
0.0
29.3
14.6
14.6
0.0
0.0
29.3
0.0
0.0
14.6
0.0
0.0
0.0
58.5
0.020
0.000
0.000
0.058
0.069
0.007
0.000
0.000
0.004
0.000
0.000
0.010
0.000
0.000
0.000
0.002
14.6
0.0
29.3
14.6
0.0
0.0
0.0
14.6
0.0
0.0
131.7
29.3
146.3
0.0
0.0
0.0
0.000
0.000
0.006
0.018
0.000
0.000
0.000
0.002
0.000
0.000
0.026
0.003
0.071
0.000
0.000
0.000
0.0
0.0
0.0
29.3
43.9
0.0
14.6
14.6
0.0
29.3
73.2
29.3
29.3
0.0
0.0
0.0
0.000
0.0
0.000
29.3
0.000
0.0
0,010 2355.4
0.021
0.0
0.000
0.0
0.002
0.0
0.002
14.6
0.000
0.0
0.019
0.0
0.015
0.0
0.010
102.4
0.037
0.0
0.000
29.3
0.000
131.7
0.000
102.4
0.000
0.002
0.000
0.146
0.000
0.000
0.000
0.003
0.000
0.000
0.000
0.904
0.000
0.001
0.022
0.002
0.000
0.000
0.000
5.871
0.000
0.000
0.000
0.000
0.001
0.979
0.483
0.000
0.000
0.000
0.000
0.002
0.000
0.000
0.017
0.039
0.429
0.000
0.006
0.000
0.000
0.004
0.000
0.000
0.000
0,000
0.000
0.000
0.014
0.0
0.0
14.6
29.3
0.0
0.0
0.0
0.0
0.0
29.3
0.0
0.0
29.3
0.0
0.0
0.0
0.0
29.3
14.6
0.0
29.3
0.0
58.5
0.0
14.6
0.0
0.0
0.0
0.0
0.0
43.9
0.0
0.0
0.000
0.000
0.014
2.617
0.000
0.000
0.000
0.000
0.000
0.640
0.000
0.000
0.023
0.000
0.000
0.000
0.000
2.211
0.062
0.000
0.012
0.000
0.017
0.000
0.008
0.000
0.000
0.000
0.000
0.000
0.008
0.000
0.000
29.3
14.6
0.0
0.0
14.6
14.6
0.0
0.0
0.0
14.6
14.6
14.6
0.0
14.6
14.6
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
43.9
14.6
0.0
73.2
0.0
43.9
0.0
0,0
29.3
0.010
0.033
0.000
0.000
0.004
0.029
0.000
0.000
0.000
0.046
1.578
0.025
0.000
0.100
0.039
0.000
0.000
0.091
0.000
0.000
0.000
0.000
0.000
0.000
0.010
0.014
0,000
0.019
0.000
0.010
0.000
0.000
0.004
0.0
0.0
43.9
0.0
0.0
14.6
0.0
0.0
29.3
0.0
0.0
14.6
0.0
0.0
0,0
0.0
117.0
0.0
0.0
0.0
0.0
14.6
0.0
58.5
14.6
14.6
14.6
14.6
14.6
58.5
0 0
0.0
0.0
0.000
0.000
0.006
0.000
0.000
0.002
0.000
0.000
0.002
0.000
0.000
0.002
0.000
0.000
0.000
0.000
0.137
0.000
0.000
0.000
0.000
0.114
0.000
0.222
0.002
0.006
0.039
0.010
0.021
0.010
0.000
0.000
0.000
0.0
0.0
14.6
0.0
0.0
0.0
14.6
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
117.0
0.0
0.0
14.6
0.0
0.0
0.0
0,0
29.3
14.6
0.0
14.6
0.0
0.0
0.0
14.6
0.0
0.000
0,000
0.004
0.000
0.000
0.000
0.008
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.072
0.000
0.000
0.014
0.000
0.000
0.000
0.000
0.008
0.015
0.000
0.006
0.000
0.000
0.000
0.695
0.000
0.000
0.0
0.182
14.6
0.013
0.0
0.000
43.9
0.029
190.2
0.000
14.6
8.724 1141.1
0.000
0.008
0,000
1.088
0.039
0.006
7.576
0.0
0.0
0.0
0.0
219.5
0.0
1316.6
0.016
0.0
0.000
0.0
0.000
0.0
0.055
58.5
0.039
131.7
0.000
0.0
3.002 3584.1
0.000
0.000
0.000
0.200
0.027
0.000
2.21~
28
3.000
0.067
32
3.029
0.070
0.000
29 3
0.000
0.0
0.000
0.0
0.000
29.3
0.019
336.5
0.000
0.0
6.698 1740.9
34
2.950
0.085
24
1.580
0.441
Appendix 2 Biomonitoring 1997
-
STATION:
QYS
N
19
8
OYS
N
20
8
OYS
N
21
B
OYS
N
22
8
0Th
N
23
8
CRUSThCEA
ANPEBREV
AtIPETENU
ARGIHANA
BATHTENU
CALLSUBT
CIROCRAN
CORYCASS
DIASBRAD
EJDOTRUN
HARPANTE
HIPPOENT
IONETHOR
ORCHNANA
PERILONG
UPOGDELT
UROTELEG
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
1.328
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
14.6
14.6
58.5
0.0
87.8
0.0
0.0
58.5
14.6
146.3
0,0
14.6
0.0
29.3
0.0
14.6
0.022
0.00
0.018
0.000
6.698
0.000
0.000
0.023
0.003
0.044
0.000
0.015
0.000
0.009
0.000
0.004
0 0
0.0
0.0
0.0
58.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.000
0.000
0.000
0.000
4.560
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
3.687
0.000
0.0
0.0
0.0
14.6
29.3
0.0
14.6
0.0
0.0
87.8
14.6
14.6
14.6
0.0
0.0
0.0
0.000
0.000
0.000
0.004
0.356
0.000
9.316
0.000
0.000
0.026
0.004
0.046
0.004
0.000
0.000
0.000
0.0
0.0
0.0
0,0
0.0
0.0
0.0
0.0
29.3
14.6
0.0
0.0
0.0
29.3
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.006
0.004
0.000
0.000
0.000
0.009
0.000
0.000
ANPHFILI
863.2
ASTRIRRE
14.6
BRISLYRI
14.6
ECHICORD
14.6
ECHIJUVE
0.0
OPHIAL8I
0.0
OPHIJUVE 2282.3
2.800
0.015
8.891
2.410
0.000
0.000
0.456
219.5
0.0
0.0
14.6
0.0
0.0
307.2
0.625
0,000
0.000
6.442
0.000
0.000
0.061
219.5
0.0
0.0
87.8
0.0
73.2
0.0
0.567
0.000
0.000
0.207
0.000
1.408
0.000
336.5
0.0
0.0
0.0
29.3
0.0
877.8
2.919
0.000
0.000
0.000
0.004
0.000
0.176
1111.9
0.0
0.0
29.3
0.0
0.0
0.0
15,499
0.000
0.000
11.932
0.000
0.000
0.000
131.7
0.0
0.0
14.6
0.0
14.6
14.6
0.0
102.4
0.0
0.0
0.0
0.0
58.5
87.8
14.6
0.0
29.3
0.0
14.6
43.9
0.0
0.0
14.6
0.049
0.000
0.000
0.002
0.000
0.003
0.008
0.000
0.125
0.000
0.000
0.000
0.000
0.025
0.018
0.003
0.000
0.007
0.000
0.002
0.004
0.000
0.000
0.001
0.0
0.0
14.6
131.7
0.0
0.0
0.0
14.6
73.2
0.0
14,6
0.0
0.0
29.3
160.9
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.029
0.027
0.000
0.000
0.000
0.004
0.023
0.000
1.494
0.000
0.000
0.016
0.032
0.000
0.003
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
29.3
0,0
0.0
29.3
0.0
0.0
0.0
29.3
0.0
43.9
43.9
0.0
0.0
43.9
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.006
0.000
0.000
0.056
0.000
0.000
0.000
0.015
0.000
0.009
0.020
0.000
0.000
0.064
0.000
0.000
0.000
0.000
0.000
43.9
0.0
0.0
14.6
0.0
0.0
14.6
14.6
29.3
43.9
0.0
0.0
0.0
0.0
160.9
43.9
0.0
43.9
131.7
0.0
0.0
14.6
14.6
0.0
0.006
0.000
0.000
0.002
0.000
0.000
0.004
0.206
0,090
0.003
0.000
0.000
0.000
0.000
0.032
0.002
0.000
0.007
0.144
0.000
0.000
0.002
0.002
0.000
43.9
14.6
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
14.6
43.9
0.0
14.6
292.6
14.6
0.0
29.3
29.3
0.0
0.0
0.0
29.3
0.0
0.005
0.002
0.000
0.000
0.003
0.000
0.000
0,000
0.000
0.000
0.495
0.004
0.000
0.032
0.058
0.002
0.000
0.007
0.090
0.000
0.000
0.000
0.031
0.000
58.5
0,0
0.0
29.3
14.6
58.5
0.0
14.6
0.0
14.6
29.3
0.0
0.0
0.0
0.0
0.0
0.0
14.6
43.9
0.0
14.6
0.0
0.0
0,0
160.9
0.0
278.0
0.0
0.0
0.012
0.000
0.000
0.012
5.056
0.124
0.000
1.939
0.000
0.010
0.008
0.000
0,000
0.000
0.000
0.000
0.000
0.001
0.270
0.000
0.017
0.000
0.000
0.000
0.620
0.000
0.031
0.000
0.000
43.9
0.0
14.6
0.0
0.0
29.3
0.0
0.0
0.0
14.6
73.2
14.6
14.6
29.3
14.6
58.5
0.0
0.0
43.9
29.3
219.5
0.0
0.0
14.6
14.6
0.0
43.9
0.0
0.0
0.014
0.000
0.006
0.000
0.000
0.127
0.000
0.000
0.000
0.004
0.048
0.031
0.095
0.023
0.012
0.008
0.000
0.000
1.338
0.004
1.396
0.000
0.000
0.039
0.006
0.000
0.008
0.000
0.000
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0,0
43.9
14.6
0.0
0.0
0.0
0.0
14.6
0.0
29.3
43.9
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.019
0.000
0.000
0,000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.006
0.056
0.000
0.000
0.000
0.000
0.077
0.000
0.251
0,006
0.000
0.000
0.0
29.3
0.0
29.3
0.0
14.6
14.6
0.0
43.9
0.0
29.3
0.0
0.0
0.0
29.3
0.0
117.0
0.0
14.6
0.0
14.6
0.0
14.6
58.5
58.5
0.0
190.2
14.6
43.9
0.000
0.006
0.000
0.010
0.000
0.079
0.001
0.000
0.014
0.000
0.010
0.000
0.000
0.000
0.234
0.000
0,031
0.000
0.127
0.000
0.004
0.000
0.031
0.218
0.019
0.000
0.025
0.001
0.014
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
43.9
0.0
0.0
0.0
0.0
0.0
73.2
0.0
43.9
0.0
0.0
29.3
0,0
0.0
0.0
0.0
234.1
0.0
0.0
0.000
0,000
0.000
0.000
0.000
0.000
0.000
0.000
0.017
0.000
0.006
0.000
0.000
0.000
0.000
0.000
0.010
0.000
0.465
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.035
0.000
0.000
ECHIN00E~J4ATA
MOLLUSCA
ABRAALBA
ACANECHI
APLACOPH
ARCTISLA
BIVALVAE
CINGVITR
COR8GI8B
CULTPELL
CYLICYLI
DOSIJUVE
D0SILUPI
EULIALBA
LEPTSQUA
HONTFERR
NYSEBIDE
NATIALDE
NATIJUVE
NUCUTENU
NUCT,JTURG
PHILSPEC
THRACONV
THRAPHAS
THYAFLEX
VENUSTRI
POLYCHA ETA
APHRACUL
API4RJTJVE
CAULLERI
CHAESETO
CHAEVARI
DIPLGLAU
EXOGHEBE
GA’fl’CIRR
GLYCNORD
GLYCROUX
GONIMACU
GYPTCAPE
HARNLUNU
LUMBLATR
MAGEALLE
MAGE,3UVE
MAGEPAP!
MEDIFRAG
NEPHHOMB
NEPHJUVE
NOTOLATE
OPHEACUM
OPHELItIA
OPHIFLEX
PECTAURI
PECTKORE
PHOLNINU
PHYLL000
PRIOCIRR
Appendix 2 Biomonitoring 1997
-
‘L.ARMI
0.0
0.000
29.3
0.010
‘AMATH
0.0
0.000
0.0
0.000
•AGRAC
29.3
0.006
43.9
0.006
080MB
0.0
0.000
131.7
0.014
OFILI
0.0
0.000
14.6
0.002
.JUVE
0.0
0.000
0.0
0.000
EKLAT
14.6
0.004
58.5
0.008
ELLANEOUS
ACLAP
0.0
0.000
14.6
2.472
‘EROPN
0.0
0.000
0.0
0.000
,FVULG
0.0
0.000
0.0
0.000
IERTIN
73.2
3.299
87.8
0.702
‘RONID
73.2
0.006
204.8
0.019
.THYHE
14.6
0.032
0.0
0.000
‘IJNCIJL
0.0
0.000
14.6
0.004
4681.4
27.591 2721.0
21.990
ERSITY
‘C
35
46
W
2.019
3.331
P
0.279
0.050
OYS
N
‘HELEG
0.0
‘HGUIL
0.0
,LJUVE
0.0
.LSUBT
29.3
.SBRAD
0.0
‘ODEFO
0.0
‘OTRUN
117.0
PANTE
0.0
PPECT
0.0
‘CINCI
0.0
HNANA
0.0
TALTA
0.0
‘TBREV
0.0
IODER14ATA
‘HFILI
0.0
‘RIRRE
0.0
ICORD
14.6
IJUVE
0.0
IPUSI
0.0
IALBI
0.0
IJT.JVE
0.0
JSCA
.AALBA
14 .3
‘TISLA
0.0
‘ALVAE
0.0
IGVITR
0.0
.BGIBB
0.0
TPELL
0.0
.ICYLI
0.0
;TR P
0.0
ITFERR
43.9
EBIDE
14.6
‘IALDE
29.3
‘UJUVE
14.6
‘UTENU
0.0
‘UTURG
0.0
SSUBT
0.0
,LFABTJ
29.3
.APHAS
0.0
IJSTRI
0.0
HAETA
IJUVE
14.6
RA Ui.,
14.6
CHIN
0.0
ESET
0.0
EVARI
0.0
LGLAU
0.0
‘SANG
0.0
TCIRR
0.0
ALBA
0.0
IMACU
73.2
NLONG
0.0
NLtJNU
0.0
ICONC
43.9
I8LATR
58.5
EJUVE
0.0
EPAPI
14.6
OYS
2
B
N
25
B
0.0
0.0
0.0
0.0
0.0
29.3
0.0
0.0
0.0
14.6
14.6
219.5
0.0
0.0
1112.1
0.000
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0,0
0.000
0.0
0.012
0.0
0.026
43.9
0.068
102.4
0.000
14.6
0.000
0.0
11.124 2984.2
21
2.633
0.103
OYS
N
58.5
14.6
0.0
14.6
0.0
0.0
14.6
0.019
0.043
0.000
0.004
0.000
0.000
0.004
14,6
14.6
0.0
14.6
0.0
0.0
0,0
0.041
0.073
0.000
0.002
0.000
0.000
0.000
0.000
0.0
0.000
14.6
0.000
0,0
0.019
14.6
0.014
43.9
0.025
0,0
0.000
0.0
14.305 2326.3
0.000
0.154
0.000
0.013
0.006
0.000
0.000
29.006
45
2.927
0.115
26
B
OYS
N
28
2.119
0,259
27
B
OYS
N
I
AN1
EDI’
Got
Got
28
B
0.000
0.000
0.000
0.305
0.000
0.000
0.023
0.000
0.000
0.000
0.000
0.000
0.000
0.
0.
0.
0.
14.
0.0
0.0
0.0
14.6
0.0
14.6
0.0
0.0
.000
.000
.000
.000
.007
0.000
0.000
0.000
0.004
0.000
0.004
0.000
0.000
0.0
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0,000
0.000
1.192
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
14
0
43.
0.
0.
29.3
0.0
146.3
0.0
0.0
0.0
0.0
0.0
0.004
0.000
0.011
0.000
0.000
0.006
0.000
0.044
0.000
0.000
0.000
0.000
0.000
117.0
43,9
14.6
0.0
0.0
0.0
14.6
43.9
0.0
14.6
0.0
29.3
14.6
0.035
0.013
0.022
0.000
0.000
0.000
0.003
0.013
0.000
0.004
0.000
0.009
0.004
0.000
0.000
0.088
0.000
0.000
0.000
0.000
0.0
0.0
0.0
190.2
0.0
0.0
263.3
0.000
0.000
0.000
0.019
0.000
0.000
0.053
292.6
0.0
29.3
0.0
0.0
43.9
541.3
1.628
0.000
0.085
0.000
0.000
0.019
0.108
0.0
14.6
0.0
0.0
0.0
0.0
87.8
0.000
0.015
0.000
0.000
0.000
0.000
0.018
0.0
0.0
0.0
0.0
292.6
0,0
73.2
0.000
0.000
0.000
0,000
0.041
0,000
0.015
0.012
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.008
0.003
0.043
0.002
0.000
0.000
0.000
0.064
0.000
0.000
29.3
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
14.6
0.0
0.0
0.0
29.3
0.002
0.000
0.002
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.009
0.052
0.000
0.000
0.000
0.002
0.0
0.0
0.0
453 5
0.0
0.0
0.0
0.0
0.0
146.3
43.9
0.0
0.0
14.6
14.6
0.0
0.0
0.0
0.000
0.000
0.000
0.045
0.000
0.000
0.000
0.000
0.000
0.029
0.030
0.000
0.000
0.162
0.014
0.000
0.000
0.000
29.3
73.2
0.0
0.0
14.6
29.3
0.0
29.3
0.0
0.0
29.3
0.0
0.0
204.8
0.0
0.0
14.6
0.0
0.025
0.007
0.000
0.000
0.003
0.251
0.000
0,004
0.000
0.000
0,018
0.000
0.000
0.125
0.000
0.000
0.006
0,000
0.0
0,0
0.0
0.0
14.6
14.6
14.6
0.0
14.6
0.0
0.0
0.0
0.0
14.6
14.6
0.0
0.0
0.0
0.000
0,000
0.000
0.000
0.047
0.000
0.002
0.000
0.003
0.000
0.000
0.000
0.000
0.145
0.006
0.000
0.000
0.000
0.002
0.309
0 000
0 000
0 000
0 000
0 000
0 000
0.000
0 010
0.000
0.000
1.222
0.106
0.000
0.004
0.0
0.0
0.0
43.9
14.6
0.0
0.0
14.6
14.6
14.6
0.0
0.0
0.0
0.0
0.0
0.000
0.000
.000
.039
2.296
.000
0.000
0.836
0.037
0.002
0.000
0.000
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
58.5
0.0
14.6
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.079
0.000
0.133
0.000
4
0.0
0.0
0.0
29.3
190.2
0.0
0.0
29.3
0.0
29.3
29.3
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.006
6.373
0.000
0.000
0.301
0,000
0.012
0.247
0.000
0,000
0.000
0.000
0.112
0.0
0.0
14.6
14.6
0.0
14.6
14.6
0.0
0.0
29.3
0.0
0.0
0.0
0.0
248.7
263.3
0.000
0.000
0.002
0.012
0.000
0.008
0.002
0.000
0.000
0.075
0.000
0.000
0.000
0.000
0.037
0.209
.
NEt
NEt
NOl
DpI.
DPI.
oNE
PAt
PEC
PHC
PoE
pot
5CC
SIC
SPI
SP3
STI’
Sn
NE~
NC
R]
SIt
SUMS
DIV
Sm
SPA
ANt
ANT
ANT
8A~
CAl
CAt
DI?
EUI
HAl
HAt
ORC
PET
ANT
AS
ECI
EU
oPT
ABI
ABi
CII
~U)
I
NY;
NY:
NA
NUt
PH
TEl
TNT
TN)
TH
TUI
V
AN’
Appendix 2 Biomonitoring 1997
-
0.0
0.000
0.0
0.000
0.0
0.000
73.2
0.029
0.0
0.000
58.5
0.0
0.0
0.0
0.0
0.0
0.0
293
14.6
0.0
0.0
0.0
307.2
0.0
14.6
0.0
0.670
0.000
0.000
0.000
0.000
0.000
0.000
0.010
0.027
0.000
0,000
0.000
0.160
0.000
0.010
0.000
0.0
29.3
0.0
0.0
0.0
14.6
0.0
0.0
14.6
14.6
0.0
0.0
14.6
0.0
0.0
73.2
0.000
0.174
0.000
0.000
0.000
0.001
0.000
0.000
0.010
0.002
0.000
0.000
0.002
0.000
0.000
0.021
14.6
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.355
0.000
0.000
0.122
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.002
0.000
0.000
0.0
0.0
0.0
0.0
0.0
0.0
29.3
14.6
0.0
0.0
365.8
0.0
73.2
0.0
0.0
87.8
0.000
0.000
0.000
0.000
0.000
0.000
0.033
0.002
0.000
0.000
0.477
0.000
0.027
0.000
0.000
0.015
14.6
0.0
14.6
0.0
73.2
0.0
0.0
0.0
14,6
0.0
0.0
29.3
248.7
0.0
0.0
0.0
0.232
0.000
0.010
0.000
0.004
0.000
0.000
0.000
0.010
0.000
0.000
0.164
0.116
0,000
0.000
0.000
0.0
0.0
0.0
0.0
14.6
43.9
0.0
0.0
1141.0
0.000
0.000
0.000
0,000
0.006
0.029
0.000
0.000
3.113
14.6
0.0
0.0
0.0
14.6
43.9
14.6
14.6
965.2
0.000
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.015
87.8
0.000
117.0
0.000
0.0
0.000
0.0
8.187 1945.4
0.000
0.000
0.000
0.000
0.225
0.019
0.000
0.000
1.485
NEPHCIRR
NEPHHONB
N T LATE
PHELIMA
PHIFLEX
OWENJUVE
PARAGRAC
PECTAURI
PHOLMINU
POECSERP
POLYDORA
SCOLARMI
SIGAMATH
SPIOBONB
SPIOJUVE
STHELIMI
SYNEKLAT
HISC~1,LAN~4JS
ANTHOZOA
EDWACLAP
GOLFELON
GOLFVULG
NEMERTIN
PHORONID
PRIAPULI
SIPUNCUL
SUMS
0.003
0.0
0.000
14.6
0.000
43.9
0.000
14.6
0.003
14.6
0.006
58.5
0.027
0.0
0.069
0.0
3.682 1901.7
0.000
0.0
0,789
0.0
1.130
0.0
0.014
0.0
0.006
29.3
0.039
0.0
0.000
0.0
0.000
0.0
5.985 1873.2
DIVERSITY
NSPC
SH’W
SIMP
STATXON~
22
2.585
0.117
26
2.611
0.129
OYS 29
B
N
21
2.189
0.172
GYS 30
N
8
27
2.839
0.083
OYS 31
N
8
31
2.791
0.088
GYS 32
N
B
OYS
N
33
8
CRUSTACEA
ANPEBREV
0.0
ANPETENU
0.0
ANPHIPOD
14.6
BATHTENU
14.6
CALLJUVE
0.0
CALLSUBT
0.0
DIAS8RAD
0.0
EUDOTRUN
0.0
HARPANTE
14.6
HARPCREN
0.0
ORCHNANA
14.6
PERILONG
14.6
ECHINODERNATA
AMPHFILI
175.6
ASTRIRRE
14 6
ECHICORD
0.0
ECHIJUVE
0.
OPHIJUVE
160.9
MOLLUSCA
ABRAALBA
43.9
ABRAJTJVE
0.0
ABRAPRIS
14.6
ACANECHI
0.0
ARCTISLA
0.0
CINGVITR
0.0
COR8GI88
0.0
CULTPELL
14.6
CYLICYLI
0.0
EULIAL8A
14.6
NONTFERR
0.0
HYSEBIDE
658.4
HYSIUNDA
0.0
NATIALDE
29.3
NUCUTURG
175.6
PHILSPEC
0.0
SPISSUBT
0.0
TELLFABU
29.3
THRAPHAS
58.5
THRASPEC
0.0
THYAFLEX
146.3
TUR8LACT
14.6
VENUSTRI
117.0
0.000
0.000
0.004
0,004
0.000
0.000
0.000
0,000
0.004
0,000
0.004
0.004
0.0
0.0
0.0
0.0
29.3
0.0
0.0
73.2
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.020
0.000
0.000
0.015
0.000
0.000
0.000
0.000
14.6
14.6
0.0
0.0
0.0
43.9
0.0
43.9
292.6
0.0
0.0
0.0
0.022
0.004
0.000
0.000
0,000
0.263
0.000
0.009
0.088
0.000
0.000
0.000
0.0
0,0
0.0
0.0
0.0
0.0
0.0
0.0
73,2
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.022
0.000
0.000
0.000
0.0
43.9
0.0
0.0
58.5
0.0
14.6
0.0
73.2
14.6
0.0
0.0
0.000
0.013
0.000
0.000
0.206
0.000
0.007
0.000
0.022
0,004
0.000
0.000
4.283
0.695
0.000
0.000
0.032
29.3
0.0
102.4
0.0
0.0
0.700
0.000
43.387
0.000
0.000
395.0
0.0
43.9
0.0
994.8
4.969
0.000
0.083
0.000
0.199
278.0
0.0
14.6
0.0
0.0
0.096
0.000
0.816
0.000
0.000
146.3
29,3
0.0
43.9
0.0
0.807
0.018
0.000
0.009
0.000
0.003
0.000
0.006
0.000
0,000
0.000
0.000
0.004
0.000
0.003
0.000
0.132
0.000
0.004
0.691
0.000
0.000
0.073
0.006
0.000
0.216
0.006
0.007
43.9
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
73.2
14.6
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.116
0.002
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.051
0.003
0.000
0.000
0.016
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
14.6
0.0
0.0
0,0
0.0
43.9
73.2
0.0
0.0
0.0
0.0
907.1
0.0
58.5
43.9
0.0
43.9
0,0
0.0
0.0
0.0
0.0
14.6
0.001
0.000
0.000
0.000
0.000
0.009
0.066
0.000
0.000
0.000
0.000
0.181
0.000
0.034
0.009
0.000
0.022
0.000
0.000
0.000
0.000
0.000
0.011
0.0
0.0
0.0
0.0
0.0
43.9
58.5
0.0
0.0
0.0
43.9
0.0
14.6
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.000
0.000
0.000
0.000
0.000
0.004
0.223
0.000
0.000
0.000
0.041
0.000
0.003
0.000
0.192
0.000
0.000
0,000
0,000
0.000
0.000
0.000
0.000
29.3
0.0
0.0
14.6
29.3
0.0
14.6
14.6
14.6
14.6
0.0
0.0
0.0
0.0
29.3
29.3
0.0
0.0
0.0
14.6
14.6
0.0
14.6
0.003
0.000
0.000
0.002
0.003
0.000
0.004
0.117
0.004
0.002
0.000
0.000
0.000
0.000
0.007
0.003
0.000
0.000
0.000
0.002
0.002
0.000
0.007
0.056
0.002
0.000
0.0
0.0
0.000
0.000
0.000
0.0
14.6
0.0
0.000
0.002
0.000
0.0
0.0
0.0
0.000
0.000
0.000
0.0
0.0
14.6
0.000
0.000
0.002
POLYCHArTA
ANAIGROE
ANAIJUVE
CHAESETO
14.6
14.6
0.0
.
Appendix 2 Biomonitoring 1997
-
CHAEVARI
0.0
CIRRATUL
0.0
DIPLGL.AU
0.0
EXOGHEBE
0.0
GA’fl’CIRR
0.0
GLYCNORD
0.0
GLYCROUX
14.6
G0NIMACU
43.9
LANICONC
14.6
LUMBLAIR
0.0
LYSILOVE
0.0
t4AGEALLE
14.6
HAGEJUVE
248,7
MAGEPAPI
0.0
MEDIFRAG
0.0
MYRIHEER
0.0
NEPHCAEC
14.6
NEPHHOMB
58.5
NEPHJUVE
0.0
NEPHLONG
0.0
NERELONG
0.0
NOTOLATE
14.6
OPHEACUM
0.0
OPHIFLEX
0.0
PARAGRAC
0.0
PECTACJRI
0.0
PECTKORE
0.0
PHOLMINU
29.3
POECSERP
0.0
POLYKINB
0.0
PRIOCIRR
0.0
PSEUPULC
0.0
SCOLARMI
14.6
SPIOBOM8
336.5
SPIOFILI
0.0
SPIOJUVE
0.0
SPIOKROE
0.0
SPIONIDA
14.6
STHELIMI
0.0
SYNEKLAT
0.0
MISCELLANEOUS
ANTHOZOA
0.0
GOLFELON
0.0
GOLFVULG
0.0
NEMERTIN
43.9
PHORONID
14.6
PLATHYHE
0.0
SUMS
2647.6
DIVERSITY
NSPC
36
2.754
SH’W
0. 107
SIMP
STATION~
OYS
N
Vg~4IAcTh
AMPETENU
BATHELEG
CALL.JUVE
CALLSUBT
DIASBRAD
EUDOTRUN
HARPANTE
HARPCREN
IONETHOR
PSEULONG
UPOGDELT
UROTELEG
0.000
0.000
0.000
0.000
0.000
0.000
0.010
0.012
0.994
0,000
0.000
0.106
0,031
0.000
0.000
0.000
0.116
2.524
0.000
0.000
0.000
0.054
0.000
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.006
0.046
0.000
0.000
0.000
0.001
0.000
0.000
0.0
0.0
29.3
0.0
0.0
0.0
0.0
14.6
0.0
29.3
14.6
0.0
0.0
43.9
14.6
14.6
0.0
29.3
0.0
0.0
14.6
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
58.5
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.004
0.001
0.000
10.149
29.3
0.0
0.0
14.6
0.0
0.0
731.5
0.000
0.000
0,054
0.000
0.000
0.000
0.000
0.002
0.000
0.085
0.701
0.000
0.000
0.029
0.002
0.002
0.000
0.044
0.000
0.000
0.004
0.000
0.072
0.000
0.000
0.000
0.000
0.000
0.000
0.100
0.000
0.000
0.000
0.048
0.000
0.000
0.000
0.000
0.000
0.000
0.0
0.0
14.6
29.3
0.0
0.0
0.0
14.6
0.0
14.6
14.6
0.0
0.0
29,3
0.0
0.0
0.0
29.3
29.3
0.0
0.0
0.0
0.0
29.3
0.0
14.6
0.0
14.6
14.6
0.0
0.0
0.0
14.6
0.0
234,1
29.3
0.0
0.0
29.3
0.0
0.000
0.000
0.004
0.002
0.000
0.000
0.000
0.008
0.000
0.046
0.097
0.000
0.000
0.008
0.000
0.000
0.000
0.137
0.004
0.000
0.000
0.000
0.000
0.054
0.000
0.004
0.000
0.004
0.004
0.000
0.000
0.000
0.006
0.000
0.039
0.002
0.000
0.000
0.125
0.000
58.5
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
43.9
0.0
0.0
14.6
14.6
29.3
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
43.9
0.0
0.0
0.0
14.6
0.0
14.6
0.0
0.0
14.6
0.0
0.0
14.6
0.135
0.0
0.000
0.0
0.000
0.0
0.006
58.5
0.000
29.3
0.000
0.0
45.673 3701.4
0.000
0.000
0.000
0.154
0.008
0.000
6.678
0.0
14.6
0.0
14.6
0.0
0.0
862.9
34
B
OYS
N
35
8
OYS
N
29.3
14.6
14.6
0.0
29.3
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
29.3
0.0
14.6
0.0
14.6
0.0
0.0
14.6
0.0
14.6
58.5
0.0
0.0
14.6
0.0
0,0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
9.965
0.019
0.014
0.000
1.668
0.002
0.000
0.000
0.000
0.000
0,000
0.000
0.000
0.000
0.000
0.000
0.000
0.994
0.000
0.019
0.000
0.589
0.000
0.000
0.002
0.000
0.143
0.019
0.000
0.000
0.002
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.004
0.000
0.0
0.010
14.6
0.000
58.5
0.010
43.9
0.000
175.6
0.000
29.3
8.072 1272.6
0.000
0.002
0.492
0.014
0.023
0.008
15.223
22
2.557
0.134
35
2.426
0.156
23
2.908
0.066
5.575
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.039
0.000
0.000
0.755
0.205
o.o08
0.000
0.000
0.000
0.000
0.000
0.000
0.010
0.000
0.006
0.000
0.000
0.000
0.004
0.000
0.004
0.000
0.000
0.048
0.000
0.000
0.002
36
B
OYS
N
39
3.317
0.052
37
B
OYS
N
38
B
0.000
0.000
0.000
3.619
0.000
0.000
0.004
0.004
0.000
0.000
0.000
0.000
14.6
29 . 3
0.0
0.0
0.0
0.0
43.9
0.0
0.0
0.0
0.0
14.6
0.004
0 . 009
0 .000
0.000
0.000
0.000
0.013
0.000
0.000
0.000
0.000
0.004
14.6
0.0
0.0
58.5
0.0
0.0
43.9
0.0
0.0
0.0
29 . 3
0.0
0.004
0.000
0.000
3.546
0.000
0.000
0.013
0.000
0.000
0,000
18.906
0.000
0.0
0.0
0.0
102.4
14.6
14.6
29 . 3
0.0
14.6
0.0
29 . 3
0.0
0.000
0.000
0.000
2.923
0.007
0.003
0.009
0.000
0.015
0.000
9.798
0.000
0.0
0.0
29.3
0.0
14.6
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.000
0.000
0.022
0.000
0.004
0.000
0.000
0.000
0.000
0.003
0.000
0.000
29.3
0.0
0,0
14.6
0.0
117.0
0.0
0.045
0.000
0.000
0.180
0.000
0.379
0.000
336.5
0.0
0.0
14.6
0.0
0.0
190.2
2.962
0.000
0.000
11.103
0.000
0.000
0.038
102.4
0.0
0.0
0.0
541.3
131.7
0.0
0.295
0.000
0.000
0.000
0.108
0.130
0.000
0.0
0.0
14.6
0.0
0.0
0.0
29 . 3
0.000
0.000
11.103
0.000
0.000
0.000
0.006
0.0
14.6
0.0
43.9
0.0
0.0
0.0
0.000
0.004
0.000
15.300
0.000
0.000
0.000
29.3
0.0
0.0
0.0
0.032
0.000
0.000
0.000
0.0
0.0
14.6
14.6
0.000
0.000
0.010
0.005
0.0
0.0
0.0
0.0
0,000
0.000
0.000
0.000
58.5
0.0
0.0
0.0
0.101
0.000
0.000
0.000
0.0
14.6
0.0
102.4
0.000
0.000
0.000
0.094
0.0
0.0
0.0
102.4
0.0
0.0
14.6
14.6
0.0
0.0
0.0
0.0
ECNINODERI4ATA
AMPHFILI
ASTRIRRE
BRISLYRI
ECHICORD
ECHIJUVE
OPHIALBI
OPHIJUVE
MOLLUSCA
ABRAALBA
ABRAJUVE
CYLICYLI
MONTFERR
Appendix 2 Biomonitoring 1997
-
MONTSPEC
0.0
0.000
0.0
0.00
0.0
0.000
29.3
0.006
MYSEBIOE
29.3
0.006
321.9
0064
0.0
0.000
14.6
0.003
NATIALDE
14.6
0.033
14.6
0.054
0.0
0.000
0.0
0.000
NUCUTTJRG
14.6
0.003
0.0
0.000
0.0
0,000
29.3
0.039
SPISELLI
14.6
0.003
0.0
0.000
0.0
0.000
0.0
0.000
SPISSUBT
0.0
0.000
0.0
0.000
0.0
0.000
14.6
0.014
TFIRAPFIAS
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.000
THYAFLEX
0.0
0 000
14.6
0.072
0.0
0.000
0.0
0.000
VENUSTRI
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.000
POLYCKA ETA
AONIPATJC
0.0
0.000
0.0
0.000
14.6
0.001
0.0
0.000
APHRACUL
0.0
0.000
0.0
0.000
14.6
0.222
0.0
0.000
APHRJUVE
0.0
0.000
0.0
0.000
0.0
0.000
14.6
0.002
CAPITELL
0.0
0.000
0.0
0.000
0.0
0.000
14.6
0.001
CHAESETO
0.0
0.000
14.6
0.006
0.0
0.000
14.6
0.004
CHAEVARI
0.0
0.000
0.0
0.000
0.0
0.000
58.5
15.749
EXOGHEBE
14.6
0.001
0.0
0.000
0.0
0.000
0.0
0.000
GA’fl’CIRR
0.0
0.000
0.0
0.000
0.0
0.000
29.3
0.587
GLYCNORO
0.0
0.000
0.0
0.000
14.6
0.001
0.0
0,000
GLYCROUX
0.0
0.000
0.0
0.000
0.0
0.000
14.6
1.093
GONIMACU
0.0
0.000
0.0
0.000
0,0
0.000
14.6
0.012
GYPTCAPE
0.0
0.000
0.0
0.000
0.0
0.000
14.6
0.014
HARMJUVE
14.6
0.004
0.0
0.000
0.0
0.000
0.0
0.000
HARMLONG
14.6
0.039
0.0
0.000
0.0
0.000
0.0
0.000
HARMLTJNU
0.0
0.000
0.0
0.000
0.0
0.000
14.6
0.100
LANICONC
0.0
0.000
0.0
0.000
73.2
0.276
0.0
0.000
LUMBLATR
14.6
0,004
0.0
0.000
58.5
0.087
14.6
0.012
LYSILOVE
0.0
0.000
0.0
0.000
14.6
0.116
0.0
0.000
t4AGEJUVE
0.0
0.000
87.8
0.006
0.0
0.000
0.0
0.000
MAGEPAPI
0.0
0.000
102.4
0.021
0.0
0.000
0.0
0.000
MEDIFRAG
87.8
0.023
0.0
0.000
14.6
0.002
58.5
0.209
NEPHHOt4B
14.6
0.539
14.6
0.662
0.0
0.000
0.0
0.000
NEPHJUVE
14.6
0.004
14.6
0.006
29.3
0.001
0.0
0.000
NERELONG
0.0
0.000
0.0
0.000
14.6
0.006
14.6
0.124
NOTOLATE
234.1
12.039
0.0
0.000
14.6
0.143
0.0
0.000
OPHIFLEX
29.3
0.093
0.0
0.000
0.0
0.000
29.3
0.091
OWENFUSI
0.0
0.000
0.0
0.000
14.6
0.004
29.3
0.087
PARAGRAC
0.0
0.000
0.0
0 000
0.0
0.000
14.6
0.001
PECTAURI
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.000
PECTKORE
0.0
0.000
0.0
0.000
0.0
0.000
58.5
0.019
PHOLMINU
0.0
0.000
0.0
0.000
43.9
0.006
14.6
0.004
POECSERP
278.0
0.290
14.6
0.010
43.9
0.017
29.3
0.012
POLYDORA
0.0
0.000
0.0
0.000
14.6
0.001
0.0
0.000
SIGAMATH
0.0
0.000
14.6
0.338
0.0
0.000
0.0
0.000
SPIOBOMB
14.6
0.002
146.3
0.043
14.6
0.004
0.0
0.000
SPIOFILI
0.0
0.000
0.0
0.000
0.0
0.000
73.2
0.014
SPIONIDA
0.0
0.000
0.0
0.000
0.0
0.000
14.6
0.001
STHELIMI
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.000
SYNEKLAT
0.0
0.000
14.6
0.006
0.0
0.000
29.3
0.002
tIISCELLANEOUS
EDWACLAP
0.0
0.000
0.0
0.000
0.0
0.000
14.6
1.097
GOLFPROC
14.6
0.019
0.0
0.000
14.6
0.265
0.0
0.000
GOLFVULG
0.0
0.000
0.0
0.000
0.0
0.000
263.3
1.684
NEMERTIN
58.5
0.023
29.3
0.021
102.4
1.495
0.0
0.000
PHORON1D
58.5
0.008
131,7
0.029
146.3
0.019
160.9
0.035
SUMS
1257.9
17.394 1609.1
15.485 1579.8
25.667 1404.2
44.977
DIVERSITY
NSPC
25
23
25
37
SH W
2.617
2.457
2.502
3.146
SIMP
.111
0,122
0.150
0.069
STATION:
QYS
N
CRI)STACEA
AMPETENTJ
ATYLFALC
BATHELEG
BATHGUIL
BATHJTJVE
BATHTENU
CALLJUVE
CAPRELLI
EU000EFO
EUDOTRUN
HARPANTE
PERILONG
PONTALTA
PSEULONG
PSEUSIMI
SYNCMACU
UROTPOSE
14.6
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
39
B
0.004
0,000
0.000
0.000
0.000
0.000
0.007
0.000
0.000
0.003
0.000
0.000
0.000
0,000
0.000
0.000
0.000
OYS
N
.0
.0
43.9
43.9
0.0
29.3
0.0
14.6
14.6
0.0
87.8
0.0
14.6
0.0
0.0
0.0
0,0
40
B
0.000
0.000
0.013
0.01
0.000
0.009
0.000
0.003
0.003
0.000
0.026
0.000
0.004
0.000
0,000
0.000
0.000
QYS
N
0.0
0.0
0.0
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
14.6
.
41
B
0.000
0.000
0.000
0.000
0.000
0.009
0.000
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0.003
0.004
0.000
OYS
N
0.0
0.0
73.2
117.0
29.3
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
.
42
B
0.000
0.000
0.022
0.035
0.006
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.022
0.0
14.6
29.3
58.5
0.0
0 0
14.6
0 0
14.6
0.000
0.003
0.005
0.031
0.000
0.000
0.004
0.000
0.002
0.0
0.0
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.0
102.4
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
102.4
0.0
0.0
14.6
0.0
0.0
14.6
0.0
0.0
14.6
0.0
14.6
29.3
0,0
43.9
43.9
0.0
0.0
14.6
0.0
0.000
0.000
0.000
0.000
0.006
0.000
0.000
0.000
0.000
0.000
0.019
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.048
0.000
0.000
0.004
0.000
0.000
0.004
0.000
0.000
0.002
0.000
0.002
0.014
0.000
0.438
0.023
0.000
0.000
0.027
0.000
0.0
0.0
0.0
14.6
0.0
804.4
0.000
0.000
0.000
0.004
0.000
16.063
24
2.883
0.071
OFF 1
N
0.0
14.6
219.5
58.5
43.9
0.0
0.0
0.0
0.0
0.0
0,0
0.0
14,6
29.3
0.0
0.0
0.0
B
0.000
0.004
0.066
0.023
0.009
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.004
0.006
0.000
0.000
0.000
Appendix 2 Biomonitoring 1997
-
WESTCAEC
14.6
ECHINODERJ4ATA
AMPHFILI
190.2
ASTEJUVE
0.0
ASTRIRRE
43.9
ECHICORD
0.0
ECHIJUVE
0.0
OPHIALBI
0.0
OPHIJUVE
146.3
I4OLLUSCA
ABRAALEA
0.0
ABRAPRIS
0.0
APLACOPH
43.9
ARCTISLA
14.6
CORBGIBB
14.6
CULTPELL
14.6
CYLICYLI
58.5
DOSILUPI
14.6
EULIALBA
0.0
GASTROPO
0.0
MONTFERR
0.0
NYSEBIDE
0.0
NATIALDE
14.6
NUCUTURG
14.6
PHILSPEC
14.6
SPISSUBT
0.0
TELLFABU
0.0
THRAPHAS
14.6
THYAFL.EX
29.3
VENUSTRI
0.0
P0LYCH~ETA
AMPHARET
0.0
ANAIGROE
0.0
ANAIJUVE
14.6
ANAIMACU
0.0
APHRJUVE
73.2
CHAESETO
29.3
ETEOLONG
0.0
GONIMACU
0.0
LANICONC
0.0
MAGEJUVE
58.5
MAGEPAPI
0.0
NEPHCIRR
0.0
NEPHHOMB
0.0
NEPHJUVE
14.6
OPHELIMA
0.0
ORBISERT
0.0
OWENJUVE
0.0
PHOLNINU
43.9
POECSERP
0.0
SCOLARMI
14.6
SCOL8ONN
0.0
SCOLJUVE
0.0
SPIOBOMB
0.0
SPIOFILI
0.0
SPIOJUVE
14.6
STHELIMI
29,3
SYNEKLAT
14.6
MISCELLANEOUS
ANTHOZOA
0.0
EDWACLAP
0.0
ENTEROPN
14.6
NENERTIN
58.5
PHORONID
0.0
SUMS
1067.6
0.004
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.000
1.043
0.000
0.015
0.000
0.000
0.000
0.029
58,5
43.9
0.0
175.6
117.0
0.0
438.9
0.502
0.015
0.000
0.077
0.012
0.000
0.088
131.7
0.0
0.0
0.0
29.3
0.0
190.2
2.294
0.000
0.000
0.000
0.003
0.000
0.038
0.0
0.0
0.0
14.6
0.0
0 0
0.0
0.000
0.000
0.000
0.102
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.000
0.000
0.000
0.000
0.000
0.198
0.000
0.000
0.000
0.044
0.002
0.020
0.002
0.097
0.004
0.000
0.000
0.000
0.000
0.107
0.081
0.003
0.000
0.000
0.002
0.037
0.000
14.6
0.0
0.0
87.8
0.0
0.0
29.3
0,0
14.6
14.6
0.0
0.0
102.4
0.0
14.6
0.0
0.0
0.0
0.0
29.3
0.002
0.000
0,000
0.015
0.000
0.000
0.392
0.000
0.003
0.003
0.000
0.000
0.050
0.000
0.003
0.000
0.000
0.000
0.000
0.053
0.0
14.6
0.0
0.0
0.0
29.3
29.3
0.0
58.5
0.0
43.9
292.6
14.6
14.6
0.0
0.0
29.3
0.0
58.5
29.3
0.000
0.013
0.000
0.000
0.000
0.011
0.002
0.000
0.006
0.000
0.047
0.058
0.002
0.169
0.000
0.000
0.004
0.000
0.137
0.021
0.0
0.0
0.0
0.0
58.5
0.0
0.0
0.0
29.3
14.6
14.6
29.3
0.0
0.0
0.0
0.0
29.3
0.0
0.0
29.3
0.000
0.000
0.000
0.000
0.012
0.000
0.000
0.000
0.006
0.002
0.017
0.006
0.000
0.000
0.000
0.000
0.043
0.000
0.000
0.002
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
0.0
14.6
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.005
0.000
0.000
0.012
0.000
0.102
0.000
0.000
0.000
0.000
0.002
0.000
0.010
0.014
0.000
0.000
0.000
0.008
0.000
0.000
0.000
0.002
0.000
0.000
0.000
0.010
0.000
0.004
0.000
0.000
0.000
0.000
0.001
0.199
0.001
14.6
0.0
14.6
29.3
73.2
73.2
0.0
14.6
0.0
365.8
599.8
0.0
0.0
0.0
0.0
0.0
14.6
131.7
0.0
497.4
0.0
175.6
468,2
0.0
43.9
14.6
14.6
0.002
0.000
0.002
0.012
0.008
0.008
0.000
0.243
0.000
0.033
0.131
0.000
0.000
0.000
0.000
0.000
0.002
0.019
0.000
0.911
0.000
0.019
0.460
0.000
0.004
0.058
0,002
0.0
29.3
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
555.9
0.0
29.3
0.0
0.0
0.0
0.0
43.9
14.6
14.6
14.6
0.0
204.8
87.8
0.0
0.0
0.0
0.000
0.050
0.000
0.000
0.000
0.000
0.000
0,006
0.000
0.000
0.089
0.000
0.535
0.000
0.000
0.000
0.000
0.006
0.006
0.004
0.062
0.000
0.033
0.014
0,000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
716.9
29.3
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
14.6
0.0
73.2
0.0
0.0
0.0
0.0
0.000
0.0
0.000
0.0
0.000
131.7
0.000
0.0
0.000
0.0
0.000
14.6
0.000
14.6
0.048
0.0
0.000
87.8
0.000
0.0
0.801 1770.2
0.077
58.5
0.000
0.0
0.000
0.0
0.006
14.6
0.000
14.6
0.000
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.068
0.0
0.000
0.0
0.050
43.9
0.000
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.000
0.000
0.019
0.000
0.000
0.006
0.004
0.000
0.871
0.000
2.875
0.120
0.000
0.000
0.006
0.043
0.000
0.000
0.000
0.000
0.000
0.000
0.027
0.000
0.000
0.000
0.000
0.000
0.0
0.000
0.0
0.483
0.0
0.000
219.5
0.002
0.0
4.113 1594.9
0.000
43.9
0.000
29.3
0.000
0.0
0.058
58.5
0.000
0.0
1.382 2721.0
19.324
0.174
0.000
0.451
0.000
24.350
0.000
0.0
0.000
0.0
0.033
0.0
0.046
29.3
0.000
453.5
1.831 4418.3
0.000
0.0
0.000
0.0
0.000
29.3
0.021
0.0
0.116
14.6
3.335 2092.1
DIVERSITY
NSPC
SHW
SIMP
30
2.987
0.074
38
2.913
0.077
30
2.661
0.118
19
2.068
0.236
22
1.566
0.436
Appendix -2 Biomonitoring 1997
STATION:
OFF 2
N
CRUSTACEA
ATYLFALC
B
OFF
N
3
B
OFF 4
N
B
OFF
N
14.6
0.004
0.0
0.000
0.0
0.000
0.0
BATHELEG
14.6
BATHGTJIL,
0.0
BATHPELA
29.3
CALLTYRR
0.0
DIA$BRA0
0.0
IPHITRIS
0.0
LEUCINCI
0.0
PERILONG
0.0
UROTPOSE
0.0
ECHINODEm4AT6
ASTATRIA
0.0
ASTERUBE
0.0
ECHICORD
0.0
ECHIPUSI
0.0
OPHIALBI
0.0
OPHIJUVE
0.0
OPHITEXT
0.0
0.004
0.000
0.009
0.000
0.000
0.000
0.000
0.000
0.000
58.5
43.9
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.018
0.O1B
0.000
0.000
0.000
0.000
0.000
0.000
0.000
14.6
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.004
0.000
0.000
0.000
0.000
0,000
0.000
0.004
0.000
102.4
0.
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
102.4
131.7
0.000
0.000
0.000
0.000
0.000
0.021
0.293
0.0
0.0
29.3
0.0
0.0
29.3
14.6
0.0
14.6
0.0
0.0
0.0
58.5
0.0
0.0
0.0
0.000
0.015
0.000
0.000
0.000
0.030
0.000
0.000
0.000
0.0
0.0
131.7
58.5
0.0
117.0
0.0
0.0
0.0
0.000
0.000
0.029
0.012
0.000
0.052
0.000
0.000
0.000
ANAIGROE
0.0
ANAIJUVE
0.0
AONIPAUC
14.6
ARICHINU
14.6
CHAESETO
14,6
ETEOLONG
0.0
EUMISANG
0.0
GONIMACU
0.0
GYPTCAPE
0.0
HARMLIJNU
0.0
LANICONC
14.6
MAGEJUVE
0.0
MAGEPAPI
0.0
NEPHCIRR
14.6
NEPHHONB
0.0
NERELONG
0.0
NOTOLATE
0.0
OPHELIMA
175.6
PECTKORE
0.0
POECSERP
0.0
SCOLARHI
29.3
SCOLBONN
0.0
SIGAMATH
0.0
SPIOBOMB
73.2
SPIOFILI
278.0
SPIOJUVE
0.0
STHELIMI
0.0
STREWEBS
0.0
TRAVFORB
14.6
MISCELLANEOUS
NEMERTIN
43.9
PHORONID
0.0
SUMS
819.2
0.000
0.000
0.004
0.006
0.008
0.000
0.000
0.000
0.000
0.000
0.081
0.000
0.000
0.006
0.000
0.000
0.000
0.139
0.000
0.000
0.066
0.000
0.000
0.135
0.089
0.000
0.000
0,000
0.112
0.0
0.0
0.0
14.6
58.5
14,6
58.5
0.0
0.0
0.0
29.3
0.0
292.6
0.0
14.6
0.0
0.0
0.0
29.3
0.0
73.2
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.000
0.000
0,000
0.008
0.012
0,004
0.010
0.000
0.000
0.000
0.265
0.000
0.382
0,000
0.129
0.000
0.000
0.000
0.836
0.000
0.467
0.000
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.013
0.000
0.720
117,0
0.0
1360.5
5
OFF 6
B
N
B
0.000
0.031
0.0
248.7
0.
14.6
14.6
29.3
0.0
234.1
0.000
0.000
0.000
0.007
0.015
0.009
0.000
0.070
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.00
0.00
3.30
0.00
0.000
0,00
0.000
0.00
0.000
0.000
5.101
0.000
0.000
0.015
0.460
0.0
14.6
43,9
0.
0.0
73.2
87.8
0.000
7.777
21.903
0.000
0.000
0,015
0.288
29.3
0.0
0.0
87.8
43.9
0.0
0.0
0.007
0.000
0.000
0.10
0.56
0.000
0.000
0.0
0.0
0.0
0.0
102.4
0.0
58.5
14.6
14.6
0.000
0.000
0.000
0.000
1.324
0.000
0.500
0.058
0,657
29.3
0.0
453.5
0.0
14.6
0.0
160.9
0.0
0.0
0.089
0.000
0.275
0.000
0.038
0.000
1.678
0.000
0.000
0.0
0.0
0.0
0.0
29.3
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.007
0.000
0.000
0.000
0.000
0.0
0.0
4.6
0.0
0.0
0.0
58.5
0.0
0.0
0.0
0.0
43.9
629.1
0.0
0.0
14.6
14.6
0.0
0.0
73.2
0.0
14,6
0.0
58.5
29.3
14.6
0.0
0.0
0.0
0.000
14.6
0.000
14.6
0.006
0.
0.000
0.
0.000
117.
0.000
14.6
0.004
29.3
0.000
14.6
0.000
29.3
0.000
117.
0.000 1784.9
0.006
0,0
0.763
234.1
0.000
0.0
0.000
29.3
0.048
29.3
0.050
292.6
0.000
0.0
0.000
0.0
0.081
29.3
0.000
87.8
0.089
0.0
0.000
14.6
0.068
58,5
0.015
43.9
0.002
0.0
0.000
29.3
0.000
0.0
0.000
0.0
0.112
0.004
0.000
0.000
0.031
0.004
0.031
0.014
0.008
0.043
6.039
0,000
0.309
0.000
2.008
1.006
5.681
0.000
0.000
0.023
0.023
0.000
0.147
0,012
0.014
0.000
0.981
0.000
0.000
0.0
14.6
0.0
0.0
0.0
14.6
0.0
0 0
0
0 0
0.0
0.0
73.2
14.6
0.0
0.0
87.8
0.0
0.0
43.9
14.6
0.0
43.9
43.9
0.0
0,0
14.6
0.0
0.000
0.004
0.000
0.000
0.000
0.006
0.000
0.000
0.000
0.000
1.207
0.000
0.000
0.452
0.180
0.000
0.000
0.541
0.000
0.000
0.056
0.438
0.000
0.052
0.015
0.000
0.000
0.004
0.000
0.190
336.5
0.000
0.0
2.748 1594.5
1.410
73.2
0.000
14.6
10.666 4345.2
0.113
14.6
0.004
160.9
48.800 1009.4
0.17
0.019
7.199
.
0.00
0.07
MOLLUSCA
ABRAALBA
CINGVITR
MONTFERR
MYSEBI0E
NATIALDE
SPISSUBT
TELLFABU
THRAPHAS
VENUSTRI
POLYCHAETA
DIVERSITY
NSPC
SH’W
SINP
16
2.142
0.181
18
2.568
0.098
21
2.126
0.213
34
2.410
0.195
19
2.494
0.117
Appendix 2 Biomonitoring 1997
-
TAPION:
0FF 7
N
OFF 8
B
N
0FF 9
B
N
OFF 10
B
N
B
OFF 11
N
B
WSTACEA
~TYLFALC
3ATHELEG
0.0
14.6
0.000
0.004
0.0
687.6
0.000
0.206
0.0
438.9
0.000
0.0
0.132 1287.4
0.0
0.000
438.9
0.176
131.7
0.053 380.4
0.0
0.000
14.6
0.002
0.0
0.000
0,0
DALL,TYRR
0.0
0.000
0.0
0.000
0.0
0.000
0.0
)IASBRAD
0.0
0.0~0
0.0
0.000
14.6
0.011
0.0
~UD0TRUN
0.0
0.000
0.0
0.000
0.0
0.000
0.0
[PHITRIS
0.0
0.000
14.6
0.015
0.0
0.000
0.0
4EGAAGIL
0.0
0.000
0.0
0.000
0.0
0.000
14.6
)RCHHUNI
0.0
0.000
0.0
0.000
0.0
0.000
0.0
‘ONTALTA
0.0
0.000
43.9
0.013
0.0
0.000
43.9
‘SEULONG
0.0
0.000
0.0
0.000
0.0
0.000
14.6
JROTBREV
0.0
0.000
0.0
0.000
58.5
0.018
190.2
)ROTPOSE
658.4
0.198
585.2
0.176
190.2
0.057
0.0
HINO0ERNATA
XHICORD
117.0
42.989
0.0
0,000
0.0
0.000
14.6
~CHIPUSI
0.0
0.000
29.3
0.025
0.0
0.000
0.0
)PHIALBI
0.0
0.000
0.0
0,000
0.0
0.000
0.0
)P[jIJtjVE
0.0
0.000
14.6
0.003
0.0
0.000
0.0
)PF4ITEXT
0.0
0.000
0.0
0.000
0.0
0.000
14.6
‘LLUSCA
~BRAALBA
0.0
0.000
0.0
0.000
0.0
0.000
14.6
~NSIARCU
0.0
0.000
0.0
0.000
14.6
35.611
0.0
O4SIENSI
14.6
1.766
0.0
0.000
0.0
0.000
0.0
IATIALDE
0.0
0.000
0.0
0.000
0.0
0.000
0.0
‘ELLFABU
0.0
0.000
234.1
6.303
0.0
0.000
0.0
‘ENUSTRI
14.6
3.507
0.0
0.000
0.0
0.000
0.0
‘LYCIIAETA
:HAE5ETQ
29.3
0.027
58.5
0.025
14.6
0.012
14.6
~TE0L0NG
0.0
0.000
14.6
0.006
0.0
0.000
0.0
~[JNISANG
14.6
0.004
0.0
0.000
0.0
0.000
0.0
;ONIMACU
0.0
0.000
0.0
0.000
0.0
0,000
0.0
YFrCAPE
0.0
0.000
14.6
0.004
0.0
0.000
0.0
IAGEJUVE
204.8
0.012
0.0
0.000
0.0
0.000
0.0
IAGEPAPI 731.5
0.765
87.8
0.100
43.9
0.185
29.3
IEPHCAEC
0.0
0.000
0.0
0.000
0.0
0.000
0.0
TEPHCIRR
14.6
0.044
43.9
0.162
43.9
0.139
14.6
IEPHHOMB
0.0
0.000
14.6
3.495
0.0
0.000
0.0
)PHELIMA
0.0
0.000
0.0
0.000
0.0
0.000
14.6
COLARNI
87.8
0.073
58.5
0.228
14.6
0.006
175.6
;COLBONN
14.6
0.079
0.0
0.000
14.6
0.127
14.6
PI0BONE
0.0
0.000
87.8
Oil)
0.0
0.000
29.3
PIOFILI
0.0
0.000
0.0
0.000
43.9
0.008
29.3
SCELLANEOUS
,NTHOZOA
14.6
0.000
0.0
0.000
0.0
0.000
0.0
IENERTIN
14.6
0.006
43.9
0.026
29.3
0.698
0.0
O4S
1945.6
49.474 2487.0
11.278 1053.3
37.056 2296.8
‘IVERSITY
ISPC
14
18
13
17
H~
1.637
2.084
1.888
1.557
‘NP
0.273
0.176
0.231
0.355
3ATHGUIL
DALLJUVE
0.000
0.386
292.6
0.088
0.152
0.000
0.000
0.000
0.000
0.000
0.004
0.000
0.013
0.003
0.057
0.000
0.0
0.0
14.6
0.0
14.6
0.0
0.0
14.6
58.5
0.0
0.0
0.0
0.000
0.000
0.009
0.000
0.003
0.000
0.000
0.004
0.018
0.000
0.000
0.000
9.591
0.000
0.000
0.000
0.058
0.0
58.5
73.2
0.0
0.0
0.000
0.053
0.476
0.000
0.000
0.053
0.000
0.000
0.000
0.000
0.000
0.0
0.0
0.0
58.5
29.3
0.0
0.000
0.000
0.000
0.222
0.010
0.000
0.041
0.000
0.000
0.000
0.000
0.000
0.137
0.000
0.056
0.000
0.402
0.521
0.405
0.008
0.019
43.9
0.0
0.0
73.2
14.6
0.0
146.3
14.6
14.6
14.6
0.0
58.5
0.0
0.0
468.2
0.002
0.000
0.000
0.363
0.001
0.000
0.174
6.730
0,131
0.151
0,000
0.027
0.000
0.000
0.274
0.000
0.0
0.000
0.0
11.908 1477.5
0.000
0.000
8.741
14.6
19
2.270
0.162
0.004
Appendix 2 Biomonitoring 1997
-
S1’ATXON:
OFF 12
N
B
OFF 13
N
B
OFF 14
N
B
OFF 15
N
OFF 16
B
N
B
CRUSTACEA
ARGIFIANA
BATFIELEG
BATI4GUIL
UROTBREV
14.6
102.4
0.0
14.6
0.004
0.031
0.000
0.004
0.0
73.2
14.6
29.3
0.000
0.022
0.006
0.009
0.0
43.9
219.5
14.6
0.000
0.013
0.088
0.004
0.0
102.4
0.0
117.0
0.000
0.031
0.000
0.035
0.0
117.0
0.0
146.3
0.000
0.035
0.000
0.044
UROTPOSE
0.0
0.000
146.3
0.044
263.3
0.079
29.3
0.009
14.6
0.004
0.0
0.0
0.0
0.000
0.000
0.000
14.6
0.0
0.0
3.010
0.000
0.000
14.6
29.3
0.0
3.010
0.031
0.000
0.0
0.0
29.3
0.000
0.000
0.001
14.6
0.0
0.0
3.010
0.000
0.000
0.0
14.6
14.6
0.0
0.0
14.6
0.0
0.0
0.000
0.009
3.674
0.000
0.000
0.163
0.000
0.000
0.0
14.6
0.0
29.3
43.9
0.0
14.6
14.6
0.000
0.015
0.000
0,078
0.181
0.000
0.234
0.002
0.0
29.3
0.0
43.9
0.0
0.0
0.0
0.0
0.000
0.014
0.000
0.035
0.000
0.000
0.000
0.000
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.145
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.0
29.3
0.0
0.0
14.6
0.0
0.0
0.0
0.000
2.604
0.000
0.000
0.018
0.000
0.000
0.000
0,0
29.3
29,3
14.6
14.6
14.6
43.9
131.7
0.0
146.3
73.2
0.0
0.000
0.002
0.006
0.017
0.043
0.006
0.263
0.294
0,000
0.039
0.019
0.000
0.0
14.6
14.6
0.0
14.6
73.2
102.4
131.7
0.0
29.3
0.0
0.0
0.000
0.002
0.002
0.000
0.046
0.220
0.149
0.160
0.000
0.019
0.000
0.000
0.0
14.6
29.3
0.0
29.3
58.5
58.5
424.3
0.0
336.5
0.0
14.6
0.000
0.002
0.006
0.000
0.058
0.137
0.041
0,780
0.000
0.224
0.000
0.035
14.6
29.3
0.0
14.6
29.3
43.9
102.4
43.9
0.0
58.5
0.0
0.0
0.019
0.002
0.000
0.027
0.075
0.145
0.158
0.149
0,000
0.031
0.000
0.000
0.0
0.0
14.6
29.3
14.6
0.0
73,2
29.3
43.9
146.3
29.3
0.0
0.000
0.000
0.010
0.037
0.019
0.000
0.185
0.058
0.176
0.199
0.041
0.000
14.6
687.5
0.039
4.612
0.0
775.4
0.000
0.0
4.205 1624.0
0.000
4.556
0.0
629.1
0.000
0.827
14.6
731.5
0.167
6.606
ECHINODEm4ATA
ECI4ICORD
OPI4IALBI
OPHIJUVE
NOLLUSCA
ABRAPRIS
DONAVIT’r
ENSIENSI
MONTFERR
NATIALDE
SPISELLI
TELLFABU
THRAPHAS
POLYCHASFA
ANAILINE
ARICHINU
CHAESETO
ETEOL.ACT
GONIHACU
F4AGEPAPI
NEPHCIRR
SCOLARMI
SCOLSQUA
SPIOBOMB
SPIOFILI
STHELIHI
HISCELLAN~US
NEMERTIN
SUMS
DIVERSITY
NSPC
SH’W
SIMP
16
2.349
0.126
17
2.461
0.109
16
2.136
0.161
13
2.330
0.115
15
2.320
0.127
Appendix -2 Biomonitoring 1997
ThTION:
0FF
N
17
B
0FF
N
18
B
0FF
N
19
B
0FF
N
20
B
0FF 21
N
B
RUSTACEA
14.6
BATHELEG
BATHGtJIL
14.6
0.0
HEGAAGIL
PONTALTA
0.0
PSEULONG
14.6
0.0
PSEUSIHI
UROTBREV
0.0
IJROTPOSE
0.0
DHIN~E~4ATA
ECHICORD
0.0
ECHIPUSI
0.0
0.004
0.006
0.000
0.000
0.003
0.000
0.000
0.000
29 . 3
14.6
29 . 3
0.0
43.9
0.0
117.0
0.0
0.009
0.012
0.009
0.000
0.009
0.000
0.088
0.000
87 . B
0.0
43.9
0.0
0.0
14.6
321.9
131.7
0 . 026
0.000
0.013
0.000
0.000
0.003
0.129
0. 040
14.6
0.0
43.9
0.0
14.6
0.0
29 . 3
0.0
0.004
0.000
0.013
0.000
0.003
0.000
0.009
0.000
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.000
0.000
14.6
0.0
33.580
0.000
29.3
0.0
22.245
0.000
0.0
0.0
0,000
0.000
0.0
14.6
0.000
0.075
0.000
0.000
0.000
0.000
29.3
0.0
0.0
0.0
0.005
0.000
0.000
0.000
0.0
14.6
0.0
0.0
0.000
0.032
0.000
0.000
0.0
0.0
14.6
0.0
0.000
0.000
0.003
0,000
0.0
0.0
0.0
29.3
0,000
0.000
0.000
0.007
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.367
0.000
0.000
0.000
0.000
0.000
0.000
0.037
0.037
0.000
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
102 . 4
0.0
0.0
0.0
0.0
14.6
0.0
29 .3
14.6
0.0
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.409
0.000
0.000
0.000
0.000
0.008
0.000
0 023
0.006
0.000
14.6
14.6
14.6
14.6
0.0
0.0
0.0
0.0
0.0
2 .3
0.0
0.0
0.0
0.0
0.0
29.3
29.3
29.3
14.6
0.002
0.006
0.006
0.048
0.000
0.000
0.000
0.000
0.000
0.288
0.000
0.000
0.000
0.000
0.000
0.415
0.052
0.012
1.058
0.0
0.0
43.9
0.0
14.6
0.0
14.6
0.0
43.9
102.4
160.9
14.6
0.0
0.0
14.6
14.6
0.0
29.3
14.6
0.000
0.000
0.008
0.000
0.008
0.000
0.021
0.000
0.332
1.234
0.019
1.275
0.000
0.000
0.048
0.460
0.000
0.014
0.504
0.0
0.0
0.0
0.0
0.0
29.3
0.0
29.3
0.0
87.8
0.0
0.0
14.6
14.6
14.6
0.0
14.6
14.6
0.0
0.000
0.000
0.000
0.000
0.000
0.002
0.000
0.002
0.000
0.510
0.000
0.000
0.002
0.002
0.004
0.000
0.006
0.025
0.000
0.000
0.000
0.000
0.454
0.0
0.0
0.0
438.9
0.000
0.000
0.000
34.156
14.6
0.0
0.0
848.6
0.006
0.000
0.000
24.380
0.0
0.0
0.0
585.0
0.000
0.000
0.000
3.954
0.0
14.6
14.6
307.1
0.000
0.003
0.001
0.643
JLLUSCA
CQRBGIBB
0.0
MONTFERR
0.0
MYSEBIDE
0.0
TELL,PYGM
0.0
DLYCKAUTA
0.0
ANAIJUVE
APHRACUL
0.0
0.0
ARICHINU
CHAESETO
0.0
0.0
ETE0LONG
EXOGHEBE
0.0
GLYCL,API
0.0
0.0
HESIAUGE
MAGEPAPI
0.0
NEPHCIRR
43.9
OPHEJUVE
0.0
OPHELIMA
0.0
0.0
PISIREHO
POLYJUVE
0.0
0.0
SCOLARHI
SCOLBONN
0.0
43.9
SPIOBOMB
SPIOFILI
43.9
TRAVFORB
0.0
ISCELLANEOUS
0.0
HYDROZOA
NEMERTIN
0.0
0.0
OLIGOCHA
17 5 . 5
—
—
DIVERSITY
NSPC
5KW
SIMP
6
1.660
0.204
11
2.098
0.156
17
2.185
0.189
16
2.372
0.132
13
2.334
0.127
Appendix 2 Biomonitoring 1997
-
STATION:
0FF 27
N
B
CRUSTACEA
BATHELEG
0.0
0.000
BATHGUIL
0.0
0.000
BATHJUVE
0.0
0.000
OIASBRAD
0.0
0.000
IPHITRIS
0.0
0.000
NEGAAGIL
0.0
0.000
QRCHNANA
0.0
0.000
PONTALTA
0.0
0.000
PSEULONG
0.0
0.000
PSEUSIMI
0.0
0.000
UROTBREV
87.8
0.035
UROTPOSE
0.0
0.000
ECKINODEN4ATA
ASTATRIA
0.0
0.000
ECHICORD
14.6
15.587
ECHIPUSI
0.0
0.000
OPHIALBI
14,6
0.877
OPHIJUVE
14.6
0.003
MOLLUSCA
ABRAPRIS
0.0
0.000
ENSIARCU
14.6
18.722
HONTFERR
43.9
0.078
NYSEBIDE
0.0
0.000
SPISELLI
0.0
0.000
TELLFABU
0.0
0.000
TELLPYGN
0.0
0.000
tOLYCHAETA
ANAIJUVE
0.0
0.000
AONIPAUC
0.0
0.000
ARICNINU
0.0
0.000
AUTOSPEC
0.0
0.000
CAPITELL
0.0
0.000
CHAESETO
0.0
0.000
ETEOLONG
0.0
0.000
EUMISANG
0.0
0.000
EUSYLLIN
0.0
0.000
GLYCLAPI
0.0
0.000
GONIBOBR
0.0
0,000
GONIMACU
0.0
0.000
HARMJUVE
14.6
0.002
HESIAUGE
0.0
0.000
LANICONC
0.0
0.000
MAGEPAPI
0.0
0.000
NEPHCIRR
58.5
0.266
NEPHJUVE
0.0
0.000
NERELONG
0.0
0.000
OPHELILIA
0.0
0.000
ORBISERT
0.0
0.000
POECSERP
0.0
0.000
PROTKEFE
0.0
0.000
SCOLARMI
234.1
1.578
SCOLBONN
14.6
0.483
SPIOBONB
43.9
0.017
SPIOFILI
0.0
0,000
SPIONIDA
0.0
0.000
MISCELLANEOUS
ANTHOZOA
0.0
0.000
BRANLANC
0.0
0.000
ECHIURUS
0.0
0.000
NEMERTIN
43.9
0.254
OLIGOCHA
0.0
0.000
SUMS
599.7
37.902
PflLEEUfl
NSPC
12
SH’W
1.992
SIMP
0.202
0FF 28
N
B
OFF 29
N
B
OFF
N
0.0
0.0
0.0
0.0
0.0
87.8
0.0
0.0
0.0
43.9
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.026
0.000
0.000
0.000
0.009
0.000
0.000
0.0
87.8
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.000
0.026
0.000
0.000
0.000
0.000
0.000
0.000
0.003
0.000
0.000
0.000
278.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
29.3
0.0
0.0
43.9
0.0
14.6
0.0
14.6
0.0
0.000
21.185
0.000
0.034
0.000
58.5
29.3
58.5
0,0
29.3
0.006
16.770
0.006
0.000
0.006
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.000
0.000
0.000
0,000
0.000
0.000
0.052
0.0
0.0
58.5
0.0
29.3
0.0
0.0
0.0
14.6
0.0
14.6
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
14.6
0.0
0.0
29.3
43.9
0.0
0.0
14.6
0.0
0.0
0.0
0.0
14.6
73.2
0.0
0.0
0.000
0.002
0.000
0.002
0.000
0.000
0.000
0.000
0.000
0.006
0.000
0.000
0.004
0.000
0.000
0.023
0.716
0.000
0.000
0.004
0.000
0.000
0.000
0.000
0.715
0.012
0.000
0.000
0.0
58.5
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
14.6
0.0
0.0
14.6
0.0
0.0
14.6
0.0
0.0
102.4
14.6
0.0
14.6
219.5
0.0
73,2
43.9
29.3
0.0
0.0
29.3
43.9
0.0
482.7
16
2.543
0.095
0.000
0.0
0.000
14.6
0.004
0.0
0.895
29.3
0 000
14.6
23.688 1038.7
23
2.777
0.086
30
B
OFF
N
31
B
0.083 1828.8
0.000
175.6
0.000
117.0
0.000
14.6
0.000
14.6
0.000
0.0
0.004
0.0
0.000
14.6
0.006
0.0
0,000
0.0
0.000
73.2
0.013
0.0
0.549
0.053
0.023
0.015
0.004
0.000
0.000
0.004
0.000
0.000
0.022
0.000
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.059
0.000
0.077
0.000
0.000
14.6
0.0
0,0
204.8
0.0
73.2
0.0
0.024
0.000
0.000
0.022
0.000
0.068
0.000
0.0
0.0
14.6
0.0
0.0
0.0
0.0
0.000
0.000
0.013
0.000
0.000
0.000
0.000
0.000
0.015
0.000
0.000
0.000
0.000
0.000
0.000
0.001
0.000
0.004
0.000
0.000
0.001
0.000
0.000
0.083
0.000
0.000
0.846
0.079
0.000
0.001
0.630
0.000
0.116
0.017
0.001
14.6
0.008
0.000
0.0
0.0
0.000
219.5
0.000
0.002
0.000
0.125
0.006
0.000
0.000
0.000
0.255
0.000
0.000
0.039
0.100
0.000
0.004
0.064
0.000
0.000
0.010
0.000
0.000
0.000
0.006
0.014
0.000
0,0
0.0
14.6
29.3
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
58.5
43.9
0.0
0.0
14.6
0.0
0.0
0.0
0.0
321.9
43.9
73.2
0.0
0.000
0.000
0.019
0.000
0.000
0.002
0.017
0.000
0.000
0.000
0.000
0.019
0.000
0.000
0.000
0.029
0.110
0.000
0.000
0.097
0.000
0.000
0.000
0.000
0.390
0.069
0.033
0.000
9.485
0.0
0.000
0.0
0.000
0.0
0.454
14.6
0.000
0.0
10.792 3101.6
0.000
0.000
0.000
0.084
0.000
1.554
0.0
0.0
0.0
14.6
0.0
14.6
14.6
0.0
0.0
0.0
29.3
0.0
0.0
14.6
131.7
0.0
14.6
29.3
0.0
0.0
29.3
0.0
0.0
0,0
73.2
58,5
0.0
0.000
14.6
0.003
0.0
0.000
0.0
0.039
175.6
0,001
0.0
18.790 1287.5
21
2.512
0.113
19
1.638
0.370
Appendix 2 Biomonitoring 1997
-
OFF 32
STATION:
N
B
OFF 33
N
B
OFF 34
N
OFF 35
B
N
OFF 36
B
N
B
cftUSTACEA
B?~THELEG
BATE4OUIL
CAPRELLI
HIPPOENT
LEUCINCI
14.6
73.2
0.0
0.0
0.0
0.004
0.022
0.000
0.000
0.000
102.4
117.0
0.0
0.0
14.6
0.031
0.035
0.000
0.000
0.004
468.2
0.0
0.0
14.6
0.0
0.140
0.000
0.000
0,004
0.000
43.9
73.2
14.6
0.0
0.0
0.013
0.022
0.003
0.000
0.000
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
NEGAAGIL
PERILONG
PSEULONG
SYNCHACTJ
UROTBREV
UROTPOSE
14.6
0.0
29.3
0.0
29.3
0.0
0.004
0.000
0.006
0.000
0.009
0.000
29.3
29.3
87.8
14.6
0.0
204.8
0.009
0.009
0.018
0.004
0.000
0.061
0.0
0.0
0.0
0.0
204.8
0.0
0.000
0.000
0.000
0.000
0.061
0.000
29.3
0.0
0.0
0.0
117.0
0.0
0.009
0.000
0.000
0.000
0.035
0.000
0.0
0.0
14.6
0.0
0.0
0.0
0.000
0.000
0.003
0.000
0.000
0.000
ECHICORD
0.0
0.000
29.3
9.887
0.0
0.000
0.0
0.000
0.0
0.000
ECHIPTJSI
OPHIALBI
MOLLUSCA
MONTFERR
SPISELLI
TELLPYGN
0.0
14.6
0.000
0.019
0.0
0.0
0.000
0.000
0.0
29.3
0.000
0.216
14.6
43.9
0.047
0.695
0.0
58.5
0.000
0.561
0.0
14.6
0.0
0.000
0.029
0.000
14.6
0.0
0.0
0.008
0.000
0.000
0.0
0.0
0.0
0.000
0.000
0.000
0.0
14.6
14.6
0.000
0.518
0.032
0.0
0.0
14.6
0.000
0.000
0.002
AONIPAIJC
0.0
ARICNINU
0.0
CAPITEL.L
0.0
ETEOLACT
0.0
ETEOLONG
0.0
EUZOFLA8
0.0
EXOGHEBE
0.0
EXOGNAID
0.0
GONIMACU
0.0
HESIAUGE
0.0
LUNBLATR
0.0
MAGEPAPI
14.6
MALDANID
0.0
MICROPHT
0.0
NEPHCIRR
43.9
NEPHJUVE
14.6
OPHEYUVE
234.1
OPHELIMA
0.0
PSA)*400R
43.9
SCOLARMI
43.9
SCOLSQUA
0.0
SPHAHYTR
0.0
SPIOBONB
0.0
SPI0FILI
43.9
SPIONIDA
0.0
STREWEBS
0.0
MISCELLANEOUS
NENERTIN
14.6
PHORONID
0.0
SUMS
643.7
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.004
0.000
0.000
0.236
0,004
0.037
0.000
0,001
0.129
0.000
0.000
0.000
0.014
0.000
0.000
0.0
43.9
14.6
0.0
14.6
0.0
0.0
0.0
14.6
0.0
0.0
29.3
0.0
0.0
43.9
0.0
0.0
14.6
0.0
58.5
0.0
0.0
0.0
0.0
0.0
0.0
0.000
0.004
0.001
0.000
0.019
0.000
0.000
0,000
0.137
0.000
0.000
0.041
0.000
0.000
0.711
0.000
0.000
0.301
0.000
0.154
0.000
0.000
0.000
0.000
0.000
0.000
0.0
73.2
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
117.0
0.0
0.0
0.0
0.0
14.6
14.6
0.0
102.4
43.9
0.0
0.0
0.000
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.131
0.000
0.000
0.149
0.000
0.000
0.000
0.000
0.023
0.168
0.000
0.164
0.069
0.000
0.000
0.0
29.3
0.0
14.6
14.6
0.0
0.0
0.0
0.0
0.0
14.6
14.6
0.0
0.0
102,4
29.3
0.0
0.0
0.0
29.3
14.6
0.0
160.9
43.9
0.0
0.0
0.000
0.002
0.000
0.048
0.001
0.000
0.000
0.000
0.000
0.000
0.019
0.108
0.000
0.000
0.666
0.001
0.000
0.000
0.000
0.396
0.029
0.000
0.048
0.004
0.000
0.000
14.6
0.0
0.0
0.0
0.0
14.6
14.6
248.7
0.0
14.6
0.0
0.0
14.6
29.3
14.6
0.0
0.0
0.0
14.6
14.6
0.0
43.9
0.0
0.0
14.6
14.6
0.001
0.000
0.000
0,000
0.000
0.001
0.001
0.015
0.000
0.001
0.000
0.000
0.001
0.001
0.892
0.000
0.000
0.000
0.001
0.039
0.000
0.002
0.000
0.000
0.001
0.001
0.010
0.000
0.527
29.3
0.0
907.0
0,045
14.6
0.000
0.0
11.480 1111.8
0.016
0.000
1,147
29.3
14.6
877.7
0.673
0.002
3.371
14.6
0.0
570.2
0.002
0.000
1.524
ECHINOOEPJ4ATA
POLYCHAETA
DIVERSITY
NSPC
15
SH’W
2.230
SINP
0.170
19
2.562
0.105
12
1.819
0.238
22
2.736
0.087
17
2.165
0.216
Appendix 2 Biomonitoring 1997
-
ITATION,
COPt 1
N
8
COA 2
N
B
COA 3
N
COA 4
B
N
COA 5
B
N
B
RUSTACEA
BATHELEG
0.0
BATHJUVE
0.0
UROTPOSE
.
CNINODER14ATA
ECHICORD
14.6
OLLUSCA
CINGVITR
0.0
ENSIDIRE
0.0
ENSISPEC
0.0
MACO8ALT
29.3
t4ONTFERR
219.5
MYSE8IDE
14,6
SPISSUBT
131.7
TELLFA8U
29.3
0.000
0.000
0.000
58.5
87.8
29.3
0.018
0.018
0.009
0.0
0.0
190.2
0.000
0.000
0.057
0.0
0.0
14.6
0.000
0.000
0.004
0.0
0.0
131.7
0.000
0.000
0.040
0.259
0.0
0.000
14.6
4.944
0.0
0. 0O0
0.000
0.000
0. 197
0.115
0.003
0. 107
0.004
0.0
58.5
0.0
292.6
0.0
29 .3
87 . 8
0.0
0.000
89.261
0.000
1.609
0.000
0.006
0.188
0.000
0.0
73.2
0.0
0.0
58.5
0.0
117.0
0.0
0.000
69.725
0.000
0.000
0.034
0.000
2.183
0.000
0.0
0.0
0.0
58.5
14.6
0.0
14.6
0.0
0.000
0.0
0.000
0.000
0.000
0,000
1.569
0.014
0.000
0,014
0.000
58.5
0.0
14.6
0.0
0.0
29.3
0.0
0.0
0.058
0.000
1.315
0.000
0.000
0 .006
0.000
0.000
0.000
0.0
0.015
497.4
0.000
43.9
0.006
0.0
0.000
0,0
0.025
0.0
0.004
0.0
0.599
58.5
0.120
0.0
0.000
14.6
0.000
0.0
0.000
14.6
0.000
29 .3
0.199
73.2
0.035
0.0
0.205
0.0
0.081 1024.1
0.000
0.154
0.025
0.000
0.000
0.000
0.000
0.044
0.000
0.021
0.000
2.408
0.004
0.166
0.000
0.000
0,237
0.0
117.0
0.0
0.0
14.6
160.9
0.0
73.2
0.0
0.0
43.9
0.0
0.0
146.3
0.0
73.2
58.5
0.000
0.029
0.000
0.000
0.004
4.548
0.000
0.029
0.000
0.000
0.164
0.000
0.000
0.139
0.000
0.029
0,031
0.0
73.2
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
73.2
0.0
0.0
0.0
0.0
0.0
102.4
0.000
73.2
0.008
336.5
0.000
29.3
0.000
0.0
0.000
0.0
0.000
14.6
0.000
0.0
0.006 2487.1
0.000
0.0
0.000
14.6
2.771
14.6
0.000
0.0
0.000
0.0
0.000
585.2
0.000
0.0
0.000
29.3
0.019
131.7
1.452
0.120
0.048
0.000
0.000
0.112
0.000
5.087
0.000
0.043
0.742
0.000
0.000
0.595
0.000
0.033
0.019
0,0000.0
81.915
365.7
0.000
43.9
4.405 3994.1
0. 187
9.856
OLYCHA Sm
ANAIMUCO
0.0
CAPICAPI
73.2
ETEOLONG
0.0
EUHISANG
14.6
HARNJUVE
0.0
LANICONC
14.6
MAGEJUVE
29.3
MAGEPAPI
219.5
NEPHCAEC
14.6
NEPHCIRR
0.0
NEPHNON8
0.0
NERELONG
0.0
OPHELIMA
0.0
SCOLARMI
87.8
SCOLBONN
14.6
SPIOBOH8
73.2
SPIOFILI
438.9
ISCELLANEOUS
NEHERTIN
14.6
UNS
1433.9
WgB~flY
NSPC
17
SH ‘ N
2.196
SIMP
0.159
~TATX0N:
0.000
0.0
94.168 1141.1
15
1,863
0,246
13
2.375
0.104
COA 7
COA 6
N
RUSTACEA
BATHELEG
8ATHGUIL
BATHJUVE
PSEULONG
UROTPOSE
OLLUSCA
CINGVITR
ENSIDIRE
MACOBALT
MYSEBIDE
SPISSU8T
TELLFABIJ
0.200
0.0
2.173 2399.4
B
N
B
8
1.808
0.188
COA8
N
B
14.6
43.9
0.0
0.0
29.3
0.004
0.013
0.000
0.000
0.009
424.3
117.0
219.5
0.0
14.6
0.127
0.035
0.044
0.000
0.004
131.7
0.
0
14
117.
0.040
0.000
0.000
0.003
0.035
0.0
14.6
102.4
0.0
14.6
0.0
0.000
17.856
1.467
0.000
0.002
0,000
29.3
0.0
160.9
0.0
0.0
0.0
0 .015
0.000
0.874
0.000
0.000
0.000
29
14.6
0.0
43.9
0.0
0.0
0.015
11.357
0.000
.009
.000
.000
ANAIMACU
0.0
CAPICAPI
819.3
ETEOLONG
0.0
LANICONC
14.6
MAGEPAPI
746.1
NEPHCAEC
0.0
NEPHHOMB
29,3
NEPHJUVE
29.3
NERELONG
0.0
SCOLARI’4I
117.0
SCOLBONN
0.0
SP1080148
585.2
SPIOFILI 1097.3
SPIOJUVE
629,1
ISCELLANEOUS
ANTHOZOA
0.0
NEMERTIN
0.0
SUMS
4286.6
0.000
b.131
0.000
0.222
0.427
0.000
0.266
0.008
0.000
0.572
0.000
0.913
0.230
0.050
0.0
146.3
43.9
0.0
438.9
0.0
43.9
0.0
0.0
14.6
0.0
0.0
73.2
0.0
0.000
43.9
0.044 2179 9
0.019
14 .6
0.000
0.
131.7
0.469
87 . 8
0.000
0.660
0.0
0.000
43.9
0.000
14.6
0.033
29 .3
0.000
14.6
0 .000
234 .1
0.015
58.5
0.000
0.0
.031
0.286
0 . 006
0.000
0.106
0.184
0.000
0.010
0.021
0.027
0.158
0.180
0.010
0.000
0.000
0.0
0.000
0.0
22.170 1726.4
0.000
0.0
0.000
14.6
2.341 3218.6
15
1.385
0.419
COA9
N
B
0.0
0.0
0.0
14.6
14.6
COPs 10
N
8
0.000
0.000
0.000
0.003
0.004
0.0
0.0
0.0
0.0
58.5
0.000
0.000
0.000
0.000
0.018
0.0
0.000
0.0
0.000
0.0
0.000
0.0
0.000
980.2 109.525
0.0
0.000
0.0
29.3
0.0
0.0
0.0
29 .3
0.000
22.707
0.000
0.000
0.000
0 . 617
OLYCHA ETA
29 . 3
43.9
0,0
14.6
117,0
0.0
0.0
58.5
0.0
43.9
0.0
0.0
29 .3
0.0
0.052
0.037
0.000
0.122
0,149
0.000
0.000
0,004
0.000
0. 166
0.000
0.000
0.006
0.000
0.0
43.9
0.0
0.0
58.5
0.0
43.9
29. 3
0.0
263.3
0,0
0.0
0.0
0.0
0.000
0.008
0.000
0.000
0.156
0.000
1.215
0.004
0.000
0.184
0.000
0.000
0.000
0.000
0.OCO
14.6
0.019
29.3
12.495 1389.8
5.172
0.055
115.294
0.0
0.0
556.0
0.000
0.000
24.908
DIVERSITY
NSPC
SH-W
SINP
15
1.937
0.174
12
2.039
0.165
18
1.416
.4
12
1.242
.1
8
1.694
0.266
Appendix 2 Biomonitoring 1997
-
STATXON:
COA 11
N
B
CRUSThCEA
ATYLSWAM
0.0
0.000
BATHELEG
0.0
0.000
I3IASBRAD
14.6
0.010
LAHPFASC
14.6
0.003
PONTAREN
0.0
0.000
IJROT8REV
0.0
0.000
UROTFOSE
102.4
0.031
ECKINOOERt4ATA
ECHICORD
14.6
0.119
OPHIAL8I
29.3
0.439
MOLLUSCA
ENSIDIRE
14.6
15.608
MYSEBIDE
0.0
0.000
SPISSU8T
29.3
0.549
TELLFABU
14.6
0.009
THRAPHAS
0.0
0.000
POLYCKAETA
CAPICAPI
0.0
0.000
CHAESETO
0.0
0.000
EUMISANG
0.0
0.000
HARMJUVE
0.0
0.000
LANICONC
29.3
1.054
LANIJUVE
0.0
0.000
MAGEPAPI
0.0
0.000
NEPHCAEC
0.0
0.000
NEPHC1RR
117.0
1.338
NEPHJUVE
0.0
0.000
PECTKORE
0.0
0.000
SCOLARMI
29.3
0.355
SCOL8ONN
14.6
0.143
SPI080M8
146.3
0.348
SPIOFILI
14.6
0.004
SPIOJT.JVE
0.0
0.000
MISCELLANEOUS
HYDROZOA
0,0
0.000
SUMS
585.1
20.090
DIVERSITY
NSPC
14
SNW
2.218
SIMP
0.146
COA 12
N
B
COA 13
N
8
COA 14
N
8
COA 15
N
8
0.0
14.6
0.0
0.0
0.0
0.0
0.0
0.000
0.004
0.000
0.000
0.000
0.000
0.000
0.0
0.0
0.0
0.0
58.5
29.3
0.0
0.000
0.000
0.000
0.000
0.018
0.009
0.000
14.6
0.0
0.0
0.0
0.0
0.0
0.0
0.004
0.000
0.000
0.000
0.000
0.000
0.000
0.0
0.0
14.6
0.0
0.0
0.0
29.3
0.000
0.000
0.009
0.000
0.000
0.000
0.009
0.0
0.0
0.000
0.000
0.0
0.0
0.000
0.000
0.0
0.0
0.000
0.000
0.0
0.0
0.000
0.000
0.0
0.0
14.6
0.0
0.0
0.000
0.000
0.096
0.000
0.000
0.0
0.0
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
29.3
29.3
14.6
0.0
14.6
65.920
0.009
0.045
0.000
0.007
87.8
0.0
43.9
14.6
0.0
61.164
0.000
3.765
0.003
0.000
0.0
0.0
0.0
0.0
0.0
0.0
160.9
0.0
117.0
14.6
0.0
14.6
14.6
14.6
29.3
29.3
0.000
0.000
0.000
0.000
0.000
0.000
0.684
0.000
0.344
0.002
0.000
0.265
0.270
0.054
0.008
0.002
0.0
0.0
0.0
0.0
0,0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
14.6
0.0
0.0
0.0
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.015
0.000
0.000
0.000
204.8
29.3
73.2
14.6
204.8
14.6
0.0
29.3
0.0
0.0
14.6
43.9
0.0
0.0
43.9
14.6
0.108
0.004
0.062
0.002
13.808
0.001
0.000
0.535
0.000
0.000
0.657
0,288
0.000
0.000
0.012
0.001
0.0
0.0
0.0
0.0
43.9
0.0
14.6
0.0
0.0
29.3
0.0
0.0
0.0
14.6
0.0
0.0
0.000
0.000
0.000
0.000
1.954
0.000
0.023
0.000
0.000
0.004
0.000
0.000
0.000
0.035
0.000
0.000
0.0
424.1
0.000
1.728
0.0
102.4
0.000
0.042
0.0
790.0
0.000
81.462
14.6
307.2
0.003
66.968
10
1.788
0.235
3
0.956
0.423
16
2.247
0.156
10
2.086
0.149
S