TISCIA 33, 45-35
GROWTH OF THE GOLDEN SPINED LOACH, SABANEJEWIA
AURATA (FILIPPI, 1865) IN RIVER TISZA (EASTERN HUNGARY)
Á. Harka, K. Györe and P. Lengyel
Harka, Á., Györe, К and, Lengyel, P. (2002): Growth of the golden spined loach [Sabanejewia
aurata (Filippi, 1865)] in River Tisza (Eastern Hungary). — Tiscia 33, 45-49.
Abstract. The paper presents data on the growth of golden spined loach, obtained on the basis of
the study of 91 fish specimens. The study material was collected from an isolated lock chamber, at
the same time and without any selection. Hence, its size and age distributions seem to represent
those of the population well.
There were 78 first-year, 12 second-year and 1 third-year fish among the collected specimens. Their
standard lengths ranged from 25 to 71 mm, their body weights, from 0.12 to 4.41. According to our
results, the average standard length of the fish at age t (L, in mm) can be expressed with the
equation L t = 92[l-e-° 505(t+001) ].
There is no significant difference between the growths of males and females. Both body length and
body weight increase intensely in the second year. Hence, the biomass of the second-year age group
is well above that of the first-year fish, in spite of the high mortality.
The reach of the Tisza studied by us is dammed, and thus, environmental conditions are not optimal
for golden spined loach. In addition, the population suffered damages also from the cyanide spill
that polluted the river in February 2000. Though, the survival of the population is not in danger, as
the species reaches maturity by the second-year age, and thus, there is an adequate proportion of
mature specimens.
Keywords: Sabanejewia bulgarica, Bertalanffy's model, age structure, mortality,
production
Á. Harka, Kossuth Lajos Secondary School, H-5350 Tiszafüred, РОВ 38, Hungary
¡
К. Györe, P. Lengyel, Research Institute for Fisheries, Aquaculture and Irrigation, H-5541
Szarvas, РОВ 47, Hungary
Introduction
The species Sabanejewia aurata was first
described from the territory of Hungary by Jászfalusi
(1948) who classified the specimens found in the
Tisza at Kőtelek into the subspecies S. a. bulgarica.
Many authors accept the existence of the subspecies
(Jászfalusi 1948, 1951, Bänärescu 1964, Bãnãrescu
et al. 1977, Balon 1967, Terofal 1997) but consensus
has not yet been developed in this respect. Numerous
authors use only the species name Sabanejewia
aurata, omitting the subspecific epithet (Müller
1983, Povz and Sket 1990, Györe 1995, Harka 1997,
Spindler 1997), while Kottelat (1997) considers valid ·
the species name Sabanejewia bulgarica.
Golden spined loach is legally protected in
Hungary from 1974. At that time, its occurrence was
proven only in the rivers Tisza (Jászfalusi 1948,
Csizmazia et al. 1965) and Danube (Tóth 1971), but
since, it has been detected from numerous rivers of
Hungary (Harka 1986, 1997; Sallai 1999a, 1999b).
Due to the secretive habits and relative rarity of the
species its biology is little known, no data on its
growth rate have been available to us up to the
present.
Material and methods
The study material consisted of 91 fish
specimens collected between September 13 and 24,
2000, from the lock chamber of an irrigation canal
branching off from the Tisza at Tiszafüred. Nets with
mesh size of 3 mm were used for sampling in order
to include even the smallest specimens.
Standard (Lc) and total length (L,) measurements
were done to the nearest millimetre, measurements of
31
weight (W) to the nearest 0.01 g. The length-weight
relationship was calculated by the formula W = a-Lb,
proposed by Tesch (1968). Age was estimated using
the Petersen method, on the basis of the length
frequency distribution, but older specimens were
aged reading the annuii of the opercular bone. Sex of
the adults was determined on the basis of the lateral
distension of the body present in the males. The
results were corroborated by dissecting the animals
and examining their gonads.
The Walford (1946) method and the Bertalanffy
(1957) model, suggested by Dickie (1968), were
applied for mathematical description of the growth.
Condition factors (CF) were calculated following
Hile (1936), biomass (В) and production (Ρ)
according to Chapman (1968). The Microsoft Excel
'97 programme was used for statistical evaluation of
the data.
Result
Length groups were formed from the standard
length data of the collected specimens using 5-mm
intervals. Presenting their frequency in a diagram,
first-year (25 to 44 mm) and older age groups are
clearly separated (Fig. 2).
50
0
Ш
20 -
η
1
с
10-
0body length (Le) mm
Fig. 2. Length-frequency of golden spined loach
Standard lengths of the fish ranged from 25 to 71
mm. Total lengths varied between 29 and 82 mm,
body weights between 0.12 and 4.41 g. The equation
describing the length-weight relationship in the golden
spined loach population was W = 3-10"6Lc 53 in
case of standard length, W = 10~6Lt3'3779 for total
length (Fig. 1).
Based on the study of the operculum, 12 of the
13 older specimens proved to be second-year (1+),
and 1 to be third-year (2+). Five males were found
among the second-year fish, with a mean standard
length of 62.6 mm, and body weight of 2.82 g. In
case of the seven females, the respective data were
63.6 mm and 2.78 g. The only third-year fish proved
to be a male. The exponentially decreasing trend in
the numbers of individuals in the age groups can be
expressed by the equation N = 762.99-e"217 (Fig. 3).
1П0
2
.c
w
о
к.
α)
.о
E
78
N = 762.99e·21784*
80 60 -
\
40 -
R2 = 0.9934
4^12
20 -
с
0 1
40
60
80
100
2
3
4
a g e (t) in s u m m e r s
l e n g t h (Lc a n d Lt) m m
Fig. 1. The length-weight relationships
Fig. 3. Age distribution of the collected specimens
Considering that total length often figures in the
results of growth studies, the relationship between
the two lengths was determined in order to facilitate
the conversion. The equation describing this relation
is L t = 1.1403LC + 1.3946.
The following average values resulted from the
actual measurements of standard and total lengths
and body weights of the study material:
First year (0+) 33 and 40 mm, 0.34 g,
Second year (1+) 63 and 74 mm, 2.79 g,
TISCIA 33
46
Third year (2+) 71 and 82 mm, 4.41 g,
respectively.
The Walford plot could be constructed using the
average standard length data of the individual age
groups, by plotting y = LC(t+i) against χ = Lc(t). The
equation of the line, fitted to the data by linear
regression analysis, is Lc(t+i) = 0.5958Lc (t) + 37.092,
on the basis of which, the asymptotic length (Linf),
indicating the maximum possible size, is 91.75 ~ 92
mm (Fig. 4).
First year (0+) 37 mm and 44 mm,
Second year (1+) 59 mm and 69 mm,
Third year (2+) 72 mm and 83 mm, respectively.
80 -
E
E
-¿60 •
•С
О)
® 40"2
л
тз
«20-
100
(О
feo
I
is 60
"E
о0
1
2
3
4
аде (t)
ê 40
Fig. 5. Growth of golden spined loach according to the
Bertalanffy model
^20
The first two age groups were represented in the
study material with a sufficient number of individuals
to allow the estimation of the instantaneous mortality
coefficient (Z), the survival rate (S) and the annual
mortality (A). The calculated values were Ζ =
1.8718; S = 0.1539 and A = 0.8461.
In the studied material, biomass of the first-year
fish (Bi) was 26.29 g, that of the second-year ones
(B2), 33,52 g. The instantaneous growth rate (G) of
weight was 2.1148. Considering that biomass grew in
the period in question, the value of G-Z, i. e. 0.2430,
was used to calculate the mean biomass ( В ) of the
sample. Based on this, В = 29.75 g.
Production (Ρ) equals the multiplication product
of the mean biomass and the instantaneous growth
rate of weight: Ρ = В xG = 62.92 g.
And finally, annual production (AP), expressed
in percentile terms, was calculated by multiplying the
P / B ratio by 100: AP = P / B · 100 = 211.5 %.
о
0
0
20
40
60
80
χ = Le (mm) at time (t)
100
Fig. 4. Growth of golden spined loach, according to the Walford
model
Standard and total lengths of the individual age
groups, calculated according to the WALFORD growth
model, were the following:
First year (0+) 37 mm and 44 mm,
Second year (1+) 59 mm and 69 mm,
Third year (2+) 72 mm and 83 mm, respectively.
Plotting against time the natural logarithms of
the differences between the asymptotic length (L¡„f)
and standard lengths reached at different ages (L,),
with all lengths expressed in millimetres, a linear plot
resulted. The equation of this was ln(Li nr L,) = -0.505t
+ 4.5133. From this, further parameters of the
Bertalanffy equation could be determined: to= -0.01
and К = 0.505.
The equation of the function describing the
growth of the golden spined loach population, on the
basis of which the average standard length (Lt) of the
t year age group can be calculated, is as follows: L, =
L¡nf[l-e" " V i . or. substituting the calculated
parameters: L t = 92[l-e- 0505(,+001) ].
Standard and total lengths for the individual age
groups, calculated according to the Bertalanffy
equation, were the following:
47 TISCIA 33
Discussion
Though the study material, consisting of hardly
100 specimens, cannot be regarded a big sample, it
seems to represent the population adequately,
considering that it was caught from one place, at the
same time, and practically without any selection.
The value of the constant b of the equations
describing the relation of length and weight - the socalled allometric exponent - was greater than 3, both
in cases of standard and total lengths. This means
that the growth rate of body weight in golden spined
loach exceeds that of their length. As a consequence,
condition of the fish improves with their age, as it
can be seen from the increasing values of the
condition factors, calculated from standard lengths
according to Hile (1936). (Table 1).
Table 1. Length, weight and condition changes in golden spined
loach
Age
0+
1+
2+
Standard
length
Lc mm
33
63
71
Total length
Lt mm
40
74
82
Body
weight
Wg
0.34
2.79
4.41
Condition
10 s CF
0.9110
1.1079
1.2321
According to Bänärescu (1964), males of golden
spined loach are hardly smaller than females. Our
experiences are in accord with this. In our sample,
the length of the second-year males was only 1 mm
shorter than that of the females. At the same time,
males are stouter because of the lateral distension of
their bodies, and thus, their body weight exceeds that
of the females in spite of their shorter size. It is
possible, however, that this situation can periodically
change. It cannot be excluded that in spring, when
eggs are fully ripened, females can take the lead in
this respect, too, although at the time of spawning the
distension situated behind the gill openings and that
in front of the dorsal fins of males also increase in
size.
Standard lengths calculated for the first- to thirdyear golden spined loach on the basis of the Walford
and Bertalanffy models used for describing and
modelling the growth, are presented in Table 2.
Lengths calculated using the two methods differ only
in tenths of millimetres, and thus, data rounded to
millimetres are absolutely identical. However, there
is a marked difference between lengths measured and
calculated for the first two age groups, which
requires explanation.
Table 2. Body lengths calculated on the basis of the
measurements with the Walford method and the Bertalanffy
equation
Age
0+
1+
2+
According to
measurements
33
63
71
Standard length (Lc) mm
According to
According to
Walford
Bertalanffy
37
37
59
59
72
72
It is clearly visible in Fig. 5. that the point
defined by the data pair of the second-year age group
is well above the y value determined by the function
Lc(t) = 0.5958Lc(t.,)+37.092, which follows from the
excellent physical development of the specimens
48
belonging to this age group. These specimens
hatched in spring of 2000, when the early and longlasting flood was accompanied by a similarly early
and long-lasting warm weather. This created
favourable conditions for an early spawning, while
the longer growth season resulted in a more intensive
development of the fry. It had been found in the fry
of pike-perch in River Tisza, too, that they grew
bigger than the average in the year in question
(Harka, 2000).
Therefore, we assume that the outstanding size
of the second-year specimens did not result from the
conditions of the year of the sampling, but of the
previous one. It can also be seen that the circumstances did not favour the growth of the first-year age
group as much as in the previous year, and thus, their
size reflects rather the conditions of worse years.
Mathematical models allow to reduce the
amplitude of incidental deviations and hence, to
show a better picture of the growth process.
Therefore, while our measured data are valid only for
the conditions of 2-3 particular years, the values
calculated according to Walford or Bertalanffy show
the average size conditions on a longer time span,
and thus, are more suitable for making predictions.
Though the annual mortality rate, which resulted
in 84.61% in our case, seems quite high, Bíró (1975)
found an even higher value (89.35 %) in first-year
bleak (Alburnus alburnus) of Lake Balaton. Taking
into consideration that the youngest generation is the
most vulnerable, these values can be considered
realistic. Mortality probably decreases in the
following year, although it can be deduced from the
trend curve of Fig. 4 that the proportion of specimens
surviving the fourth-year age must be negligibly
small in the population. Therefore, the life span of
golden spined loach in the studied reach of the Tisza
can be put at 4-5 years.
In our case, estimation of biomass and
production was possible only for first- and secondyear fish. Lacking other data that would allow
comparison, we can record only that weight gain was
very rapid in the period in question (the weight gain
rate was considerably higher than the values common
in older generations). Hence, biomass grew in spite
of the high mortality, and the annual production was
above 200 %.
In conclusion, it seems - partly from our
previous observations, partly on the basis of our
experiences on other waters - that the environmental
conditions in the dammed reach of River Tisza
studied by us are not really favourable for the golden
spined loach. Hence, the number of older (third- to
fourth-year) specimens is little, and, according to our
subjective evaluation, they do not attain the size of
TISCIA 33
fish inhabiting waters that provide more favourable
conditions. However, the proportion of mature
specimens still reaches the level necessary for the
stability of the population, and thus, this population
of golden spined loach is not immediately
endangered.
Harka Á. (1997): Halaink [Fishes of Hungary]. — Természet- és
Környezetvédő Tanárok Egyesülete, Budapest, 175 p.
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