APPENDIX
3.
Investigation of distribution and biomass
of the comb jelly Mnemiopsis in coastal zone of the Azerbaijan sector of the
Caspian Sea
Dr. Z.M. Kuliyev
Director of AzerNIRKH
No doubts that a comprehensive study of the
new invasive species, which is threatening the biological resources of the Caspian, is
urgently needed.
The disastrous results of the Mnemiopsis
invasion into the Sea of Azov give rise to concerns of potential destruction of trophic
systems in the South, Middle and partly North Caspian ensuing its invasion into this sea.
The claim is made by certain scientists (Volovik, 2000) that unless large scale and
efficient actions were taken to control development of the population of Mnemiopsis,
the unique natural system and important fisheries of the Caspian would be lost.
Considering that commercial fisheries of the Caspian have incurred heavy losses after
invasion of the comb jelly due to a sharp drop in sprat catches, there is an urgent need
to develop a common, scientifically substantiated, action plan to save the ecosystems of
the Caspian Sea from detrimental impact of the invasive comb jelly Mnemiopsis.
By accounts of researchers, the ctenophore
was found in the Caspian in 1997-1998. All Caspian jellyfishes (endemics of the Caspian
and those, which penetrated earlier) occur in small numbers and they dont have a
significant effect on the total biomass of food organisms of the Sea. A considerable
growth of the biomass of Mnemiopsis was recorded in the South and the Middle
Caspian in 2000, along with a drop in the biomass of mezoplankton (Shiganova et al. 2000;
Sokolskiy, Shiganova, Zykov 2001).
The workshop, which was
held in Baku (24-26 April 2001) to discuss the problem of the invasion into the Caspian of
the comb jelly Mnemiopsis, boosted attention to this problem. The workshop noted
that large-scale development of Mnemiopsis in the Caspian Sea could have a
disastrous effect on the whole biota of the sea. First of all, a biological explosion of
the new invader can radically change the species composition and biomass of mezoplankton,
and be followed by a decrease in numbers of the most abundant commercial species
sprats and all other pelagic species. In view of a high percent of endemic species among
the animals of the Caspian Sea, and the outcomes of the invasion of Mnemiopsis into
the Black Sea, one can conclude that the biological diversity of the Caspian is under
serious threat. Therefore, the working group, which was established to study this
ctenophore in the framework of the Caspian Environment Programme (CEP), prepared a
Methodology to study the invasion of Mnemiopsis and other jelly-like organisms into
the Caspian Sea for environmental impact assessment of the ctenophore on the ecosystem of
the Caspian Sea. In this regards, the initiative and actions undertaken by the CEP to
study this organisms deserve special attention.
Taking into account that the invasion of
the ctenophore indeed imperils fish stocks of the Caspian, the Azerbaijan Research
Institute of Fisheries developed a research program in April 2001 to study distribution,
abundance and biomass of the jellyfish in the Azerbaijan Sector of the Caspian Sea and
submitted it for consideration of the CEP leadership. Having considered the work program
provided by our Institute, experts of the CEP suggested to the leadership of their program
supporting the Institute in conduct of the entire research program.
The research program includes conduct of
surveys at the following five stationary transects in the Middle and South Caspian
Yalama, Siazan, Primorsk, Neftchala and Lenkoran (depths 0-25m), at existing permanent
observation stations of the Institute. Besides, it was also planned to take samples at
additional transects, marked on the map (see map).
The following stations were chosen and
approved:
- Yalama coast (settlement Yalama 6);
- Siazan (set. Zarat);
- Sangachaly (set. Primorsk);
- Neftchala (Kura estuary); and
- Lenkeran (port Liman).
It was decided to conduct initial studies
at several stations at transects that comprise the whole coastal zone at depths of 3, 5
and 10m, and also at the depth of 25m, where safety measures allow.
All equipment and methodology were agreed
with CEP experts, which held several joint researches with the personnel of the institute
(A. Kideys).
Abiotic factors of the environment were
also measured: temperature, salinity, transparency and oxygen content in water at all
transects and depths (Table 1).
Studies and sampling started in July and
have been continuing up to the present. Mnemiopsis of different size and age groups
was found at all transects. The highest biomasses of Mnemiopsis were recorded at
the stations in the vicinity of Sumgayit (Jorat) - at the depth of 10m (up to 271,0 gm/m3),
at the settlement Shikhovo at the depths of 3m (up to 247,8 gm/m3), at
the settlement Liman (137,0 gm/m3) and in Siazan at the depths of 5m
(151,9 gm/m3). More than 7 thousand specimens of ctenophore were processed
during this period.
An analysis of Mnemiopsis
distribution by size groups in the summer (July-August) of 2001 showed that smaller size
groups with the length up to 15mm prevailed all along the coastline (Table 2) averaging to
89.1% (from 70.7 to 98.8%).
It should be noted that the size
composition strongly varied. The biggest specimens of jellyfish of the size group 61-65mm
were found singly. However, small specimens (young and juvenile stages) constituted more
than 70% at the majority of transects. Complete predomination of small specimens (91,3%)
was observed in Lenkeran at the depth of 10m.
In autumn the studies were extended and
comprised 10 transects. An analysis of size characteristics showed that the number of
ctenophores of smaller age groups even more increased and size ranges narrowed. The major
part of the population consisted of specimens with the length up to 10mm, they fluctuated
from 71.1 to 100% and making 86.3% in average. The minimal concentrations of the
ctenophore were recorded at northern transects (Yalama and Khachmaz), and a trend of
southward increase of abundance was noted (Table 3).
The high content of young specimens
testifies of relentless reproduction during 4 months (July-October).
The November samplings conducted at seven
transects showed a considerable reduction in abundance of Mnemiopsis, amounting to
less than 5% of the previous values. Mnemiopsis was not found at certain transects
(Borisovs bank, Kura estuary) at all or was found but singly. However, at the same
time, more than 60% of the whole material was collected only at the transect Liman (Table
4).
All data pertaining to spread, abundance
and size-weight composition of the ctenophore in the coastal zone of the Azerbaijan sector
of the Caspian Sea were filled into a special database, created for this purpose.
Analyses of samples of zooplankton revealed
scarcity of species composition of plankters. Copepods were represented only by one
species - Acartia clausi, which dominated among other plankton organisms. Other plankton
organisms included larvae of nereis, mollusks and balanus (Table 5).
Feeding habits of the ctenophore and its
qualitative and quantitative parameters by size groups were also studied in accordance
with the work program (Table 6).
As it shown in the table below, the species
composition of ctenophores diet corresponds to that of zooplankton.
Feeding of sprats taken in summertime at
the Borisovs bank was characterized by the following parameters (Table 7): 54,5% had
empty alimentary tracts, 33,4% of alimentary tracts were filled with singly specimens of Cypris
balanus and only 9,1% had medium filling of alimentary tracts. The coefficient of
fatness of sprats (by Clark) was low. All analyzed specimens of sprats were at the fifth
stage of maturity of genital products, which was reflected in their coefficient of fatness
by Fulton.
The research provided the following
preliminary results:
- Mnemiopsis
is ubiquitous all over the coastal zone in
the Azerbaijan sector of the Caspian Sea;
- The highest biomass and abundance of the ctenophore was
recorded in July-September;
- Juvenile comb jellies prevailed in all samples (length range
up to 15mm in summer 88,1%; up to 10mm in autumn 86,3%); the maximal size of
adult specimens was 61-65mm; and
- The range of food consumed by comb jellies entirely matched
to the species composition of zooplankton as well as the range of food of plankton-eating
fish, the biomass of plankton has a direct relationship with the abundance of comb
jellies, whose biomass by far exceeds that of plankton.
- We believe it would be useful to conduct regular seasonal
monitoring, which will allow for determining the major stages of development of Mnemiopsis
(outset and end of active period, terms and periodicity of reproduction, etc.);
- Conduct cameral studies of comb jellies relation with
abiotic environmental factors (temperature, salinity, oxygen) and range of feeding;
- Conduct of comprehensive studies of relationship of Mnemiopsis,
Beroe and plankton organisms for the purpose of potential introduction of Beroe
in the Caspian to reduce abundance of Mnemiopsis.
The proposed studies will allow for
obtaining more detailed and conclusive information on the biology and distribution of Mnemiopsis,
and will serves as the basis for development of a program for abatement of adverse
consequences of its introduction on the biota of the Caspian Sea.
Table 1. Abiotic factors of the
environment
Month |
Temperature
(C°) |
Salinity
(%0) |
Transparrency |
|
Min. |
Max. |
Mean |
Min. |
Max. |
Mean |
Min |
Max. |
Mean |
June |
24.0 |
27.0 |
25.61 |
|
|
|
0.25 |
5.0 |
2.17 |
Aug. |
25.5 |
27.5 |
26.57 |
|
|
|
1.2 |
6.0 |
3.07 |
Sep. |
25.3 |
28.1 |
17.01 |
7.9 |
11.5 |
11.2 |
0.5 |
6.5 |
2.71 |
Oct. |
19.4 |
23.7 |
21.22 |
10.0 |
11.5 |
10.89 |
1.0 |
4.2 |
2.22 |
All |
19.4 |
28.1 |
25.1 |
7.9 |
11.5 |
10.96 |
0.25 |
6.5 |
2.54 |
Month |
pH |
O2 (dissolved,
mg/l) |
O2 (saturation,
%) |
|
Min. |
Max. |
Mean |
Min. |
Max. |
Mean |
Min |
Max. |
Mean |
June |
7.9 |
8.2 |
7.88 8.07 |
|
|
|
|
|
|
Aug. |
|
|
|
|
|
|
|
|
|
Sep. |
8.0 |
8.48 |
8.27 |
5,6 |
7.2 |
6.15 |
61.7 |
74.2 |
66.36 |
Oct. |
7.2 |
8.4 |
8.05 |
4.1 |
7.3 |
5.68 |
48.1 |
72.5 |
59.37 |
All |
7.2 |
8.48 |
8.07 |
4.1 |
7.3 |
5.91 |
48.1 |
74.2 |
62.86 |
Table 5. Qualitative
indicators of zooplankton in shallow waters of the Middles and South Caspian in July 2001
(specimens/mg/m3)
Primorsk
(30.07.01) |
3 |
5 |
8 |
10 |
Acartia clausi |
|
14\0.91 |
4\0.26 |
2\0.13 |
Acartia clausi (naupli) |
|
3\0.006 |
- |
- |
Nereis larvae |
|
- |
- |
- |
Bivalvia larvae |
|
- |
- |
- |
Cirripedia cypris + larvae |
|
8\0.008 |
- |
- |
Jellesis |
|
- |
- |
- |
Total: |
|
25\0.92 |
4\0.26 |
2\0.13 |
Siazan
(26.07.01) |
3 |
5 |
10 |
25 |
Acartia clausi |
|
46\2.99 |
11\0/715 |
|
Acartia clausi (naupli) |
|
15\0.03 |
8\0/016 |
|
Nereis larvae |
|
- |
+ |
|
Bivalvia larvae |
|
9\0/045 |
3\0/015 |
|
Cirripedia cypris + larvae |
|
6\0/006 |
3\0\003 |
|
Jellesis |
|
- |
- |
|
Total: |
|
76\3/071 |
25\0.744 |
|
Yalama
(24.07.01) |
3 |
5 |
10 |
25 |
Acartia clausi |
29\1.89 |
52\3.38 |
22\1.43 |
6\0.39 |
Acartia clausi (naupli) |
5\0.01 |
7\0.014 |
5\0.01 |
3\0.006 |
Nereis larvae |
- |
+ |
+ |
+ |
Bivalvia larvae |
- |
4\0.002 |
1\0.005 |
- |
Cirripedia cypris + larvae |
13\0.013 |
10\0.01 |
2\0.002 |
2\0.002 |
Jellesis |
- |
- |
- |
- |
Total: |
47\1.913 |
73\3.406 |
30\1.438 |
7\0.45 |
Liman
(01.08.01) |
3 |
5 |
7 |
10 |
Acartia clausi |
127\8.255 |
|
28\1.82 |
7\0.455 |
Acartia clausi (naupli) |
31\0.062 |
|
- |
- |
Nereis larvae |
- |
|
- |
- |
Bivalvia larvae |
+ |
|
- |
- |
Cirripedia cypris + larvae |
5\0.005 |
|
- |
- |
Jellesis |
- |
|
- |
- |
Total: |
163\8.32 |
|
28\1.82 |
7\0.455 |
Table 2. Characteristics of size groups
of Mnemiopsis by transects of the Middle and South Caspian (%)
Summer 2001 (July-August)
Size groups
(mm) |
Yalama |
Siazan |
Shikhovo |
Primorsk |
Liman |
Total |
0 5
6-10
11-15 |
43,5
15,9
11,3
subtotal 70.7 |
48,2
24,5
10,1
subtotal 82.8 |
67,6
18,3
12,9
subtotal 98.8 |
60,5
22,1
8,4
subtotal 91.0 |
53,4
20,6
12,3
subtotal 86.3 |
58,4
19,5
11,2
subtotal 89.1 |
16-20 |
8.4 |
3.6 |
1.0 |
2.3 |
7.4 |
3.5 |
21-25 |
7.8 |
3.6 |
- |
2.7 |
3.8 |
2.8 |
26-30 |
4.1 |
2.9 |
0.2 |
1.8 |
2.0 |
1.8 |
31-35 |
4.3 |
1.4 |
- |
1.2 |
0.5 |
1.3 |
36-40 |
1.4 |
0.7 |
- |
0.6 |
- |
0.5 |
41-45 |
1.8 |
1.4 |
- |
- |
- |
0.4 |
46-50 |
0.9 |
- |
- |
0.4 |
- |
0.3 |
51-55 |
0.6 |
2.2 |
- |
- |
- |
0.3 |
56-60 |
- |
0.7 |
- |
- |
- |
- |
61-65 |
- |
0.7 |
- |
- |
- |
- |
Number
(spec.) |
345 |
139 |
712 |
488 |
204 |
1888 |
Table 3. Characteristics of size groups of
Mnemiopsis by transects of the Middle and South Caspian (%)
Autumn 2001 (September-October)
Size groups
(ìì) |
Yalama |
Khachmaz |
Siazan |
Sumgayit |
Primorsk |
Bandovan |
Kura estuary |
Borisovs
bank |
Liman |
Narimanabad
- 2 |
Total |
0 5
6-10 |
86.57
13.3
subtotal 100.0 |
100,0
- |
83,4
10,3
subtotal 93.7 |
65,7
5,4
subtotal 71.1 |
67,0
17,5
subtotal 84.8 |
48.5
42,5
subtotal 91.0 |
55,7
32,0
subtotal 87.7 |
94.8
4,1
subtotal 98.9 |
96,2
3.2
subtotal 99.4 |
95,8
1,6
subtotal 97.4 |
82,2
6,1
subtotal 86.3 |
11-15 |
- |
- |
4.9 |
14.7 |
7.8 |
3.0 |
5.1 |
0.9 |
0.3 |
2.3 |
5.8 |
16-20 |
- |
- |
1.1 |
7.4 |
1.0 |
- |
- |
- |
0.3 |
0.3 |
3.2 |
21-25 |
- |
- |
0.3 |
4.5 |
5.8 |
1.6 |
2.1 |
0.2 |
- |
- |
1.8 |
26-30 |
- |
- |
- |
1.4 |
- |
2.2 |
1.0 |
- |
- |
- |
0.5 |
31-35 |
- |
- |
- |
0.4 |
- |
- |
2.1 |
- |
- |
- |
0.2 |
36-40 |
- |
- |
- |
- |
- |
2.2 |
1.0 |
- |
- |
- |
0.1 |
41-45 |
- |
- |
- |
0.3 |
0.9 |
- |
0.9 |
- |
- |
- |
0.1 |
46-50 |
- |
- |
- |
0.2 |
- |
- |
- |
|
- |
- |
- |
51-55 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
56-60 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
61-65 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Number
(spec.) |
15 |
17 |
368 |
1699 |
103 |
134 |
97 |
344 |
1144 |
1123 |
5044 |
Table 6. Food composition of Mnemiopsis
in shallow waters at western coast of the Caspian Sea
Summer 2001
Size group of Mnemiopsis |
Organisms |
Average per specimen |
Number
of specimens |
Weight,
mg |
Total
(mg) |
- Large specimens
(L = 2.8-3.6 mm)
TOTAL 7 specimens
|
Acartia
clausi
Bivalvia larvae
Hydrozoa
Cirripedia cypris
+ naupli |
211
43
2
13 |
13,715
0,215
0,002
0,013 |
13.945 |
- Small specimens
(L = 0.0-8.0 ìì)
Total 15 specimens
|
Acartia
clausi
naupli
Bivalvia larvae
Cirripedia cypris
+ naupli |
47
15
17
8 |
3,055
0,030
0.085
0.008 |
3.178 |
Table 4. Characteristics of size groups of
Mnemiopsis by transects of the Middle and South Caspian (%)
November 2001
Size groups
(mm) |
Yalama |
Siazan |
Primorsk |
Shikhovo |
Kura estuary
|
Borisovs
bank |
Liman |
Total |
0
5 |
92,3 |
56,6 |
64,7 |
43,0 |
50,0 |
|
85,2 |
73,4 |
6-10 |
7,7 |
30,1 |
29,4 |
49,4 |
50,0 |
|
10,9 |
20,8 |
Total |
100.0 |
86.7 |
94.1 |
91.4 |
100.0 |
|
96.1 |
94.2 |
1-15 |
|
3,8 |
5,9 |
6,3 |
|
|
3,2 |
3,8 |
16-20 |
|
3,8 |
|
1,3 |
|
|
0,7 |
1,1 |
21-25 |
|
1,9 |
|
|
|
|
|
0,2 |
26-30 |
|
3,8 |
|
|
|
|
|
0,7 |
31-35 |
|
|
|
|
|
|
|
|
36-40 |
|
|
|
|
|
|
|
|
41-45 |
|
|
|
|
|
|
|
|
46-50 |
|
|
|
|
|
|
|
|
51-55 |
|
|
|
|
|
|
|
|
56-60 |
|
|
|
|
|
|
|
|
61-65 |
|
|
|
|
|
|
|
|
Total: |
13 |
53 |
17 |
79 |
2 |
0 |
284 |
448 |
Table 7. Feeding of
plankton-eating fish (sprat) at western coast of the Caspian Sea
Summer 2001
¹ |
L
(ñì) |
L
(ñì) |
P
(ãð) |
P
(ãð) |
Sex |
Organisms
|
Filling
of stomach |
Fultons
Coefficient |
Clarks
Coefficient |
Sprat,
Borisovs bank, depth of 25-50 m |
1 |
9.8 |
8.2 |
3.85 |
3.0 |
_- |
Cypris balanus |
Medium |
0.7 |
0.54 |
2 |
10.5 |
9.0 |
5.05 |
3.97 |
_- |
Cypris balanus |
Empty |
0.69 |
0.54 |
3 |
10.4 |
8.7 |
4.82 |
4.1 |
_- |
- |
Empty |
0.73 |
0.62 |
4 |
11.1 |
9.2 |
5.6 |
4.35 |
+ |
- |
Empty |
0.72 |
0.56 |
5 |
9.9 |
8.0 |
4.2 |
3.6 |
+ |
Cypris balanus |
Singular |
0.82 |
0.7 |
6 |
9.0 |
7.6 |
3.2 |
2.6 |
+ |
- |
Empty |
0.73 |
0.59 |
7 |
9.5 |
8.1 |
4.25 |
3.55 |
_- |
- |
Empty |
0.8 |
0.67 |
8 |
9.6 |
8.3 |
3.95 |
3.36 |
_- |
- |
Empty |
0.69 |
0.59 |
9 |
10.6 |
8.9 |
5.25 |
4.73 |
_- |
- |
Empty |
0.74 |
0.67 |
10 |
9.7 |
7.4 |
3.5 |
2.45 |
_- |
Cypris balanus |
Singular |
0.86 |
0.6 |
11 |
10.6 |
8.9 |
5.35 |
4.4 |
_- |
Cypris balanus |
Singular |
0.76 |
0.62 |
54,5 % - empty, 36,4 % - singular, 9,0 %
- medium
|