Knowledge and Management of Aquatic Ecosystems (2009) 394-395, 08
c ONEMA, 2010
DOI: 10.1051/kmae/2009022
http://www.kmae-journal.org
Effect of chloride content in water on heart rate
in narrow-clawed crayfish (Astacus leptodactylus)
P. Kozák(1) , T. Policar(1) , V.P. Fedotov(2) , T.V. Kuznetsova(2) , M. Buřič(1) ,
S.V. Kholodkevich(2)
Received September 25, 2009 / Reçu le 25 septembre 2009
Revised December 7, 2009 / Révisé le 7 décembre 2009
Accepted December 11, 2009 / Accepté le 11 décembre 2009
ABSTRACT
Key-words:
cardiac activity,
Astacus
leptodactylus,
crayfish,
heart rate,
chloride
A non-invasive method of recording cardiac activity was used to examine the impact of chloride level in water on narrow-clawed crayfish. This
method permits one to record heart rate without any harm to the animal,
and also locates changes in the shape and amplitude parameters of the
response, which characterized the crayfish functional state. Altogether,
eight levels of chloride (100, 400, 800, 1600, 3200, 6400, 12 800 and
25 600 mg·L−1 NaCl) were evaluated. Already at low levels some crayfish
were influenced. A clear reaction was evident starting from 3200 mg·L−1
NaCl. On the contrary, crayfish showed a high tolerance to high chloride
levels, and the heart rate and stress index returned to normal within a few
minutes or hours after NaCl addition.
RÉSUMÉ
Effet de la concentration de l’eau en chlorure sur la fréquence cardiaque chez l’écrevisse
à pattes grêles (Astacus leptodactylus )
Mots-clés :
activité
cardiaque,
Astacus
leptodactylus,
écrevisse,
fréquence
cardiaque,
chlorure
Une méthode non-invasive d’enregistrement de l’activité cardiaque a été utilisée
pour étudier l’impact de la concentration de l’eau en chlorure chez l’écrevisse à
pattes grêles. Cette méthode permet l’enregistrement du rythme cardiaque sans
dommage pour l’animal et détermine également les changements dans la forme
et l’amplitude des paramètres de la réponse, qui caractérise l’état fonctionnel de
l’écrevisse. Au total, huit concentrations de chlorure (100, 400, 800, 1600, 3200,
6400, 12 800 et 25 600 mg·L−1 NaCl) ont été testées. Quelques écrevisses sont
influencées dès les basses concentrations. Une réaction claire a bien été mise en
évidence à partir de 3200 mg·L−1 NaCl. Par contre, l’écrevisse montre une forte
tolérance aux concentrations élevées de chlorure et la fréquence cardiaque et
l’indice de stress reviennent à la normale en quelques minutes ou heures après
l’addition de NaCl.
INTRODUCTION
The morphology and physiology of the crustacean cardiovascular system have long been regarded as poorly organized and loosely controlled, and serving only as a conduit to carry
(1) University of South Bohemia in České Budějovice, Faculty of Fisheries and Protection of Waters, Zátiši 728/II,
389 25 Vodňany, Czech Republic, kozak@vurh.jcu.cz
(2) St. Petersburg Scientific Research Centre for Ecological Safety, Laboratory of Experimental Ecology
of Aquatic Systems, Korpusnaja str., 18, Saint-Petersburg 197110, Russia
Article published by EDP Sciences
P. Kozák et al.: Knowl. Managt. Aquatic Ecosyst. (2009) 394-395, 08
hemolymph. This view was based on early comparisons between the closed and open
cardiovascular systems found in vertebrates and crustaceans, respectively. Further studies
of the cardiovascular systems of decapod Crustaceana, however, have revealed a system
that is more complex than previously thought. Hormonal and neural regulation of cardiac
contractility, cardiac contraction frequency and cardioarterial valve tonus via the cardiac ganglion and pericardial organ have been demonstrated, e.g. in the crab Cancer magister (Airries
and McMahon, 1992). Furthermore, cardiovascular responses towards environmental pertubations have also been identified (e.g. Airries and McMahon, 1994; Reiber et al., 1997; Reiber
and McMahon, 1998).
Despite being freshwater animals, crayfish can also live in environments subject to variation
in salinity. They are adaptable animals, tolerating a wide range of environmental variables
(McMahon, 1986). For example, Cherkasina (1975) reported that Astacus leptodactylus survives in waters with salinity levels of 14 in the Caspian Sea and feeds on a variety of brackishwater organisms. Köksal (1988) found A. leptodactylus on the Baltic coast, and in the Black
and Caspian Seas. Holdich et al. (1997) reported that Austropotabomius pallipes, A. leptodactylus and Pacifastacus leniusculus were capable of hyper-regulating their hemolymph
osmotic pressure up to approximately 50% seawater, and hyporegulate at higher salinities.
Some evidence was presented that crayfish growth might be improved by low salinities, possibly because less energy is being used for osmoregulatory purposes (Newsom and Davis,
1994). Rouse and Kartamulia (1992a, 1992b) reported that 100 mg·L−1 NaCl had a positive
effect on acclimatization, molting success and survival of Cherax tenuimanus. Higher chloride
concentrations also have favorable effects on the toleration of aquatic organisms to nitrate.
The mechanism is well described (e.g. Morris, 2001; Kirschner, 2004). Positive effects of chloride aiding tolerance to nitrites have been demonstrated in fish (Hilmy et al., 1987; Atwood
et al., 2001; Huertas et al., 2002; Fuller et al., 2003; Tavares and Boyd, 2003) and crayfish
(Beitenger and Huey, 1981; Jeberg and Jensen, 1994). Crawford and Allen (1977) showed that
toxicity of nitrite depended on water salinity. For example, the value of 96hLC50 increased
from 5 mg·L−1 of nitrites in tap water to 97 mg at a level of 400 mg·L−1 Cl− for Orconectes
limosus (Kozák et al., 2005).
On the contrary, crayfish could serve as good bioindicators, with quick reactions to several chemical changes and stimuli (Kholodkevich et al., 2008). Evaluation of the physiological
state involves measurements of heart rate and cardiac activity patterns as key indicators of
the conditions of the patient, and are included in all general clinical assessments in medical science (Swash and Mason, 1984). Numerous authors have found heart rate to be a
useful indicator of changes in physiological state, even in crustaceans, molluscs and fish
(e.g. Depledge and Andersen, 1990; Kholodkevich et al., 2008).
In this study we use a non-invasive method to evaluate the impact of chloride level in water
on cardiac activity, as an indicator of physiological stage, in narrow-clawed crayfish.
MATERIAL AND METHODS
The experiment was conducted in the Laboratory of Experimental Ecology of Aquatic Systems, Saint-Petersburg Scientific Research Center for Ecological Safety (SRCES RAS) during
September 2006.
> EQUIPMENT
An original fiber-optic method for recording cardiac activity of Crustacean (Decapoda) and
Mollusca (Fedotov et al., 2000; Kholodkevich et al., 2008) was used to measure the impact of
chlorides on crayfish cardiac activity. A block-scheme of cardiac activity registration, signal
transformation and automatic data processing in real time is depicted in Figure 1.
The infra-red light beam initially formed in the laser fiber-optic photoplethysmograph (LFOP)
is transmitted to the animal by a thin optical fiber with a small sensor (weight less than 2 g)
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P. Kozák et al.: Knowl. Managt. Aquatic Ecosyst. (2009) 394-395, 08
Figure 1
Block-scheme of cardiac activity registration, signal transformation and automatic data processing in
real time. LFOP: laser fiber-optic photoplethysmograph, DSO: digital storing oscilloscope, PC: personal
computer, SD: standard deviation, HR: heart rate, SI: stress index.
Figure 1
Schéma du système d’enregistrement de l’activité cardiaque, de transformation du signal et de traitement en temps réel des données. LFOP : photoplethysmographe à fibre optique-laser, DSO : oscilloscope digital de stockage, PC : ordinateur, SD : déviation standard, HR : fréquence cardiaque, SI :
indice de stress.
attached to the carapace, thus illuminating the heart area with a scattered light. The optical signal modulated by the heart of the animal contains information on cardiac activity.
After appropriate amplification and filtration in the LFOP, the analog signal is then transmitted
to the digital storing oscilloscope (DSO), where it is converted into digital form by a 14-bit
16-channel analog-digital converter (ADC). Thereafter it is send to a personal computer (PC)
via a USB port. The results create a photoplethysmogram, which can be further analyzed by
various mathematical and statistical methods. An original software program, VarPulse , automatically reads data from the ADC, determines the duration of each cardiac interval in real
time (block 1), and calculates a set of heart rhythm variability characteristics. The variation
pulsometry (VP) method was used to study the distribution of cardiac intervals, and analyzed
relationships between its shape and the functioning of the cardiac system (Figure 2). For
this method the following characteristics were chosen as biomarkers: heart rate (HR) and the
stress index (SI), which is defined by the formula (Kholodkevich et al., 2007, 2008):
SI = 1/(2 ∗ CIm ∗ SD2 ),
(1)
where CIm = means cardiac interval, which is related to HR, with HR = 60/CIm ; SD = standard
deviation of heart rate.
> ANIMALS AND EXPERIMENTAL CONDITIONS
Sixteen narrow-clawed crayfish, originating from Sevan lake (Armenia), were used in the
experiment. The animals were acclimatized for three weeks before the experiment to the
controlled conditions. They were kept in two troughs (2.5 × 0.5 × 0.3 m) with shelters in
a recirculating system. During the experiment, each crayfish was maintained in a separate
5-liter aquarium with a shelter, which allowed the crayfish (with sensor and fiber attached)
to stay inside (Figure 3). The total radius of the animal’s migration (25 cm) was restricted
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P. Kozák et al.: Knowl. Managt. Aquatic Ecosyst. (2009) 394-395, 08
Figure 2
Variation pulsometry method to study relations between cardiac system functioning and the cardiac
interval distribution law.
Figure 2
Méthode d’étude des relations entre le fonctionnement du cœur et la distribution des intervalles de
pulsation.
Figure 3
Narrow-clawed crayfish (Astacus leptodactylus) in 5-liter aquarium with a shelter, which allowed the
crayfish with a sensor (1) and fiber (2) attached to stay inside.
Figure 3
Écrevisse à pattes grêles (Astacus leptodactylus) dans un aquarium de 5 L avec un abri, où l’écrevisse
avec détecteur (1) et fibre (2) peut s’abriter.
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P. Kozák et al.: Knowl. Managt. Aquatic Ecosyst. (2009) 394-395, 08
only by the size of the aquarium. The water level was set at 15 cm. Crayfish were not fed
during the experiment, and each animal was used only once. Water quality parameters were
as follows: temperature 22 ◦ C, oxygen content 80–100% sat, pH 7.5, HCO−3 32.5 mg·L−1 ,
−1
−
−1
2+
SO2−
11.3 mg·L−1 , Mg2+ 2.9 mg·L−1 , Na2+ 3.3 mg·L−1 , K+
4 19.3 mg·L , Cl 7.8 mg·L , Ca
−1
1.5 mg·L . The experiment was performed in the daylight period in September (D:N = 14:10).
> EXPERIMENTAL DESIGN
We tested the following eight levels of chloride content: 100, 400, 800, 1600, 3200, 6400,
12 800 and 25 600 mg·L−1 NaCl. Each level was evaluated in two replicates. Animals were
stocked in the evening of the day before the experiment to acclimatize to the new conditions.
The relevant amounts of NaCl, dissolved in 100 mL of water, were introduced to aquariums
the following day when crayfish were in a tranquil stage (after stabilizing of heart rate and
stress index for at least one hour). Crayfish were exposed to chloride for 24 h.
> DATA ANALYSIS
The non-parametric one-tailed Wilcoxon test was used to compare HR and SI before and
after stimulation, with the level of significance at which the null hypothesis was rejected at
α = 0.05. Data are presented as means ± 95% confidence intervals.
RESULTS
Some crayfish already showed a reaction at the lowest application levels of chloride. One
crayfish had a slightly increased heart rate, but it was not reflected by the stress index. A clear
stress index reaction just after NaCl addition was characterized by an increase during the first
20 min in both crayfish subjected to 400 mg NaCl. However, only in one of them was a
significant difference in heart rate confirmed (Table 1; Figure 4). The stress index decreased
after 20 min, and the heart rate stabilized to normal.
Interestingly, both heart rate and the stress index increased only slightly immediately after
stimulation at 800 and 1600 mg NaCl, but increased rapidly after the following 40 min. A very
clear reaction in heart rate and the stress index was evident from the level up to 1600 mg·L−1
NaCl (Figure 5). Reactions were rapid and clear for both heart rate and the stress index.
On the contrary, crayfish showed a high tolerance to high chloride content in water, and
heart rate and the stress index returned to normal within a few minutes or hours after NaCl
addition, depending on the dosage of NaCl. Only at the highest concentrations (12 800 and
25 600 mg Cl− ·L−1 ) did heart rate stabilize for a longer time.
DISCUSSION
In addition to a high sensitivity to changes in water quality, narrow-clawed crayfish
showed a relatively high tolerance to water salinity. The highest concentration of chloride
(25 600 mg Cl− ·L−1 = 42 g NaCl) corresponds to its content in seawater (35 g·L−1 ). With concentrations inside ranges for brackish water (0.6–10 g·L−1 ), heart rate and the stress index
returned to normal within one hour. These results confirmed the high tolerance and adaptability of narrow-clawed crayfish to high salinities reported by Cherkasina (1975) and Köksal
(1988). However, at higher concentrations (up to 12 800 mg Cl− ·L−1 , which corresponds to
21 g of NaCl), recovery of crayfish was delayed. Normally, freshwater fish and crustaceans
are hyperosmotic to their environment. This phenomenon could be related to the capability of
crayfish to hyper-regulate their osmotic pressure up to approximately 50% of seawater, and
hyporegulation at higher salinities, as reported by Holdich et al. (1997).
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Table I
Comparison of heart rate and stress index of narrow-clawed crayfish (Astacus leptodactylus) before and after stimulation in different chloride concentrations. The
different superscripts between columns before and after stimulation indicate statistical difference (P > 0.05).
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Crayfish
A
B
C
D
E
F
G
H
I
J
K
L
M
N
O
P
Concentration
Cl− [mg·L−1 ]
100
100
400
400
800
800
1600
1600
3200
3200
6400
6400
12 800
12 800
25 600
25 600
Heart rate – median
Before stimulation
After stimulation
65.22a
64.66a
41.11b
46.53a
a
58.82
55.17b
b
51.11
60.91a
b
50.04
53.69a
42.22a
39.46b
b
59.85
69.05a
b
46.40
51.95a
26.48b
90.77a
b
44.49
53.57a
b
74.81
87.85a
b
42.14
49.30a
32.90b
58.94a
b
52.43
80.00a
b
44.91
85.11a
64.45b
93.75a
Wilcoxon test
Z
P
0.35
0.727
−6.80
< 10−6
8.25
< 10−6
−4.45
< 10−5
−7.88
< 10−6
5.00
< 10−5
−7.72
< 10−6
−10.79
< 10−6
−12.56
< 10−6
−13.16
< 10−6
−18.61
< 10−6
−10.70
< 10−6
−6.64
< 10−6
−15.75
< 10−6
−15.25
< 10−6
−17.30
< 10−6
Stress index – median
Before stimulation
After stimulation
411.30a
327.67b
66.20a
66.53a
b
200.94
231.45a
b
7.17
96.51a
a
152.20
92.78b
77.69a
56.89b
b
360.38
453.51a
b
26.57
117.45a
9.79b
304.50a
b
75.98
110.99a
b
474.55
756.05a
b
45.97
108.82a
20.53b
91.52a
b
216.59
1034.47a
b
58.25
977.07a
296.80b
2256.16a
Wilcoxon test
Z
P
2.86
0.004
0.23
0.816
−3.01
0.003
−6.29
< 10−6
6.40
< 10−6
4.55
< 10−5
−3.09
0.002
−8.58
< 10−6
−11.80
< 10−6
−5.87
< 10−6
−10.28
< 10−6
−6.17
< 10−6
−6.11
< 10−6
−14.31
< 10−6
−14.59
< 10−6
−15.02
< 10−6
P. Kozák et al.: Knowl. Managt. Aquatic Ecosyst. (2009) 394-395, 08
Tableau I
Comparaison de la fréquence cardiaque et de l’indice de stress chez l’écrevisse à pattes grêles (Astacus leptodactylus) avant et après exposition à différentes concentrations en chlorure. Les différentes lettres entre colonnes avant et après exposition indiquent les différences statistiques (P > 0,05).
P. Kozák et al.: Knowl. Managt. Aquatic Ecosyst. (2009) 394-395, 08
Figure 4
The course of heart rate and stress index of individual narrow-clawed crayfish (Astacus leptodactylus)
one hour before and after stimulation (x-axis in minutes), respectively, at different chloride concentrations. The addition of salt into the water is marked as the time of 0:00.
Figure 4
Suivi de la fréquence cardiaque et de l’indice de stress d’individus de l’écrevisse à pattes grêles (Astacus
leptodactylus) une heure avant et après la stimulation (axe des x en minutes) à différentes concentrations
en chlorure. L’ajout de sel à l’eau est fait au temps 0:00.
The high tolerance of crayfish to chloride is highly applicable in aquaculture, especially with
the use of recirculation systems subject to a risk of high concentrations of nitrate. Fish and
crayfish actively take in ions via the gills to counteract their loss through urine and passive
outflow. Nitrite has an affinity for the active chloride uptake mechanism by chloride cells in
the gills (Maetz, 1971). Chloride cells excrete ammonia or H+ ions in exchange for Na+ ions,
and bicarbonate (HCO−3 ) for Cl− ions (Love, 1980). NO−2 has affinity to Cl− /HCO−3 exchanging.
A part of the Cl− demand is replaced by NO−2 when present in water. Fish with a higher rate
of chloride uptake by gills (rainbow trout, perch, pike) are more sensitive to nitrites compared
to species with a lower rate of chloride uptake (eel, common carp, tench) (Williams and Eddy,
1986). The competition between chloride and nitrite ion transport across the gill membrane
explains that the higher concentration of Cl− protects animals against the toxic impact of
nitrite (Jensen, 2003). In seawater a fifty- to hundredfold lower mortality was observed than
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P. Kozák et al.: Knowl. Managt. Aquatic Ecosyst. (2009) 394-395, 08
Figure 5
The course of heart rate and stress index of individual narrow-clawed crayfish (Astacus leptodactylus)
one hour before and after stimulation (x-axis in minutes), respectively, at different chloride concentrations. The addition of salt into the water is marked as the time of 0:00.
Figure 5
Suivi de la fréquence cardiaque et de l’indice de stress d’individus de l’écrevisse à pattes grêles (Astacus
leptodactylus) une heure avant et après la stimulation (axe des x en minutes) à différentes concentrations
en chlorure. L’ajout de sel à l’eau est fait au temps 0:00.
in fresh water at the same concentration of nitrite. The relationship between nitrite toxicity
and chloride concentration is linear (Russo and Thurston, 1977; Kozák et al., 2005).
In conclusion, this study confirmed the high tolerance of narrow-clawed crayfish to high salinity, which is important both from an ecological and aquaculture point of view. Secondly, we
proved that crayfish could be a good bioindicator, which could be used together with suitable
analyzing equipment to monitor water quality, e.g. by industrial water companies.
ACKNOWLEDGEMENTS
This investigation was financially supported by the Czech Ministry of Education (projects USB
RIFCH No. MSM6007665809 and ME 855) and the Ministry of Agriculture (project QH71305).
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