Bull. Eur. Ass. Fish Pathol., 36(4) 2016, 169
ȱȱȱȱ ȱȱȱCyprinus carpio M. Witeska*, K. Lugowska and E. Kondera Department of Animal Physiology, Siedlce University of Natural Sciences and Humanities, Prusa 12, 08-110 Siedlce, Poland
Abstract ¢ȱȱȱȱȱȱȱȱȱȱęȱȱȱ¢ȱǰȱȱȱȱȱǯȱ ǰȱȱȱȱȱ ȱȱęȱȱȱȱĜȱȱȱȱȱȱȱȱ¢ȱȱȱ spatial, temporal and individual variability. In the present paper we summarized the data obtained ȱŘŖŖŜȬŘŖŗŚȱȱȱȱȱŚŗȱȱŗŚŜȱǻȱȱǼȱ¢ȱ¢ȱȱǰȱ śȬŞȱȱȱǰȱȱȱȱȱȱȱȱȱȱȱ¢ȱ ¢ȱ¢ȱȱřȬŚȱ ȱȱŗŜȬŗŞǚǯȱȱşśƖȱęȱȱȱȱȱȱ DZȱ ȱŘŚǯŖȬŘśǯśƖǰȱ ȱŜŘǯŚȬŜşǯŜȱȦǰȱȱŗǯřśȬŗǯśŗȱƼȱŗŖ6ȦΐǰȱȱŗŝŞǯŜȬŘŖŖǯŗȱǰȱ ȱŚŝǯřȬśřǯŗȱ ǰȱ ȱŘśŜǯŜȬŘŞŚǯşȱȦǰȱ¢ȱȱ¢ȱŘǯŗȬŚǯŗƖǰȱȱśŗǯřȬŜŖǯŞȱƼȱŗŖ3Ȧΐǰȱ¢ȱ DZȱ¢¢ȱŞŝǯřȬşŗǯŝƖǰȱȱśǯŜȬŞǯşƖȱȱ¢ȱŖǯŝȬŘǯŖƖǰȱȱŗŚǯŚȬŘśǯŚȱƼȱŗŖ3Ȧΐȱ ȱȱ¡ȱȱ¢ȱȱ¢ȱŖǯşŗȬŗǯŗŗȱȦȱȱ£ǯȱȱȱ ȱȱěȱ¢ȱȱȱȱǰȱȱȱȱȱȱ ǻǯǯȱ¢ȱȱ¢¢ǼǰȱȱȮȱ¢ȱȱǻȱ ǰȱǰȱǰȱ ȱȱ Ǽǰȱ ȱȱȬȱ¢ȱȱǻȱȱȱ¢ȱȱ¢Ǽǯ
Introduction Hematological analyses including complete ȱȱȱȱȱȱȱ or immunological parameters are sometimes ȱȱȱȱęȱȱȱ¢-
ȱȱȱȱ¢ȱȱęȱȱ ȱƹȱŗǯşŜȱȱȱ¢ȱȱȱ or values at 2.5 percentile and 97.5 percentile ȱȬ¢ȱȱǯȱ
ȱȱȱ¢ȱȱȱȱȱȱ ǰȱȱęȱȱȱȱ ¢ȱȱȱǯȱ
ǰȱȱęȱȱȱȱ
ȱȱ¢ȱȱȱȱȱ
ȱȱȱ¢ȱȱ ȱȱȱȱ¡ȱȱȱ
ȱȱşśƖȱęȱȱȱȱ ǰȱ¢ȱ¡ȱȱȱȱĴȱ
ȱȱȱȱĜȱȱȱȱ vertebrates due to their poikilothermy and
which water temperature plays probably the
ŘǯśƖȱȱȱȱȱȱǻȱ et al., 2010). According to Ambayya et al. (2014),
most important role. According to Leard et al. ǻŗşşŞǼǰȱȱȱȱȱȱ¢ȱ
ȱȱȱȱȱ-
vary a single baseline range is appropriate,
* Corresponding author’s e-mail:
[email protected]
170, Bull. Eur. Ass. Fish Pathol., 36(4) 2016
ȱȱȱȱ ȱȱȱ Ěȱȱȱ¢ȱȱȱȱȱ¢ȱȱǯȱȱȱ ȱǻŗşşśǰȱŗşşŝǼǰȱȱȱȱȃȄȱ ȱȃȱȄȱȱȱȱęȱ ȱ¢ȱȱȱȱȱȱ¢ȱęȱ ěȱ ȱǯȱȱȱȱ-
ȱȱȱȱȱ ȱȱ£ȱȱ own data concerning hematological parameters ȱ¢ȱ¢ȱȱȱȱȱ similar size and age, reared in pond and then acclimated to the laboratory environment, colȱȱȱȱȱşȱ¢ǯ
tological parameters may considerably vary
Materials and methods
ȱȱȱȱȱȱȱ
ȱȱȱȱȱśȬŞȱ
ȱěȱ¢ȱȱȱǻȱ ȱȱǯǰȱ 2001; Svetina et al., 2002; Bastami et al., 2009)
months old clinically healthy common carp
and environmental (eg Orun and Erdemli, 2002; Morgan et al., 2008; Langer et al., 2013; Gupta et
60.7 g were collected and evaluated. The results ȱȱȱŚŗȬŗŚŜȱ¢ȱȱȱ ȱęǰȱȱȱŘŖŖŜȱȱŘŖŗŚȱǻȱȱ-
ǯǰȱŘŖŗřǼȱǯȱȱȱȱǻŗşşśǼǰȱ ȱDZȱǰȱȱȱȱȱthyohematology should be replaced by wider ȱȱ¢ȱȮȱȱȃ¢ȱȄǯȱ ǰȱȱȱȱȱęȱȱ ȱȱȱ¡ȱȱȱ
(Cyprinus carpioǼȱȱ¢ȱȱ ȱŘŖǯŜȬ
ȱ ȱȱȱȱęǼǯȱȱęȱ ȱȱȱȱȱȱȱȱ Inland Fisheries Institute in Zabieniec or the ¿ȱȱȱȱ ǰȱǰȱ ȱȱȱȱȱȱȱǰȱȱ
be always compared with appropriate with-
ȱȱ¢¢ȱȱęȱ ȱ
Ȭ¢ȱǯȱȱȱȱȱ
water and supplied with pure oxygen to the
ȱǰȱȱȱȱęȱȱȱȱȱęȱȱȱ
¢ȱȱȱȱȱȱ¢¢ǰȱȱ¢ȱȱȱȱ
ȱęȱȱǰȱȱ
ȱ ǯȱȱȱęȱȱȱ
help to improve study design, and reduce the
groups were subjected to ichthyopathological
ȱȱȱȱȱȱȱȱȱ
examination including clinical, anatomopatho-
experimental and control groups.
logical, parasitological and bacteriological eval-
Common carp belong to the most popular
ȱȱȱȱȱȱ¢ȱȱ ¢ȱȱȱȱȱȱ
ȱęȱȱȱȱ ȱȱȱ
ȱǯȱȱęȱȱ ȱȱ
also widely used in pond and laboratory exǯȱ ȱȱȱȱ
ȱřȬŚȱ ȱȱȱĚ Ȭȱȱȱ 250 L at water temperature 16-18oC, and were
common carp were evaluated by many authors ǻȱŗǼȱȱȱȱȱȱ¢ȱ-
¢ȱȱȱŗȱ ȱȱ¡ȱȱǻŗŖȬŗŘȱęȱȱŗŖŖȱǼȱȱ ȱ
ȱȱȱȱȱȱȱǯȱȱȱȱȱ ȱȱȱ
water was changed daily by siphoning out 75%
used as control groups in their experiments and ěȱ¢ǰȱ¢ȱȱȱȱȱ ȱǯ
ȱȱȱȱ ȱȱnated tap water. Water quality parameters in ȱȱ ȱȱ¢ȱȱ ȱ renewal. The water temperature in aquaria was similar as in the acclimation tank (16-19oC),
34±1 28±0.5 29±3 44.0±6.0 43.6 43.6±0.18 33.6±3.2 31.8±5.5 22-39 29±3 36±6 26±3 22.0±5.3 29.8±2.7 33.1-34.8 34.7±2.5 27.2 13.7-13.8 31.0±0.5 15.6±1.5 41.5±0.6 29.2±2.7 42.2±0.5 30.9±3.5 22.3±1.4 42.8±4.0
Ht [%]
Hb [g/L]
MCV [fL]
1.27±0.05 91±4 2.00±0.28 55±6 78.3±2.1 2.31±0.16 103.7±0.6 1.81±0.2 69.4±16.0 178.2±31.7 0.90-2.02 37.6-87.6 133.7–248.4 1.64±0.14 86.3±7.6 180.3±15.3 1.68±0.26 98.2±15.4 236.2±24.6 1.05±0.03 68.4±9.2 248.1±36.0 1.51±0.01 70.7±15.2 1.58±0.10 50.0±0.0 189.3±4.2 1.56-1.65 56.5-61.2 202.7-216.7 1.51±0.22 88.6±4.6 190.0±40.0 1.40-1.49 52.2-53.4 186.5-198.0 0.33-0.38 46.3-47.2 367.3-413.7 2.60±0.01 84.0±10.0 1.07±0.09 - 130.9±16.3 2.48±0.20 88.8±10.0 1.63±0.13 74.30±7.35 179.5±13.5 1.80±0.02 112.4±.4.1 234.5±2.0 2.94-2.95 83.8-84.6 1.40±0.09 71.8±13.5 217.2±24.2 2.30±0.2 60 ±3 1.18±0.06 1.37±0.19 94±8 317.9±60.9
RBC [103/μL] 40.2±6.5 36.9–57.8 52.9±4.7 58.8±6.9 65.2±10.0 31.8±2.0 36.1±38.7 54.0±17.2 34.9-39.8 125-139 45.8±4.2 62.5±1.6 51.9±8.2 -
WBC [103/μL] 18 15.5 23±2 22 21.0±1.5 17±1 19.5-19.9 16.5-17.9 27.4±0.4 26.2–27.1 22.5 38.6±0.8 18-26 27.0±1.2 21-24 23±1 23±1 16.8–20.1 20±1 19±2 21.2 25±0.2
Ù ȱȱ ǰȱŗşşŖ Yildiz, 1998 Kopp and Hetesa, 2000 ÚȱȱǯǰȱŘŖŖŖ Stosik et al., 2001 Svetina et al., 2002 Harikrishnan et al., 2003 Tripathi et al., 2004 Mikula et al., 2008 Sudova et al., 2009 Velisek et al., 2009 Velisek et al., 2010 Ajani and Akpoilih, 2010 Kumar et al., 2010 Ahmad et al., 2011 Al Ghanim, 2011 Enache et al., 2011 Saravanan et al., 2011 Al-Rudainy and Kadhim, 2012 Gul et al., 2012 Pakravan et al., 2012 Velisek et al., 2012 Gholami-Seyedkolaei et al., 2013 Masud and Singh, 2013 Yonar, 2013 Jagruthi et al., 2014 Jahanbakhshi et al., 2014 Kuhlwein et al., 2014
Age/mass Water Author ȱęȱǽǾ temp. [°C]
58.8±8.0 62±12 37.8±2.9 26.8±2.9 120±3 36.9±7.9 60-80 20-50 57.3 3.2±0.1 40±10 216±33 24.0±5.6 200 150-320 61.2±7.3 290±20 74.0±28.3 138.3±28.7 257±26 8.2±3.7 15.3±4.6 263±13 85.4±15.5 138.3±28.7 1.4±0.1 19.4±14.1 171±28 143.0±10.0 2-3 171-179 35.5-37.2 55-60 295±13 - Fingerlings 191-196 65-66 293-337 16.8-18.5 8.0±0.4 25.4±0.9 40-50 4.2±4.1 50.9±11.0 2.9±0.8 20±2 255±11 20.5±7.8 297.4±55.6 266±7 22.0±0.1 41.0±0.2 - 18.4-18.5 11.5-19.5 241±31 32.7±3.2 67.5±9.1 - 155.1±2.0 26.3±1.4 9.9±0.2 25 222±33 29.7±7.1 61.9±2.4
MCH MCHC [pg] [g/L]
Table 1.ȱȱȱǻƹǯǯǼȱȱȱȱȱȱȱCyprinus carpio (according to various authors).
Bull. Eur. Ass. Fish Pathol., 36(4) 2016, 171
172, Bull. Eur. Ass. Fish Pathol., 36(4) 2016
Thangam et al., 2014 Wang et al., 2014 Yonar et al., 2014 Bojarski et al., 2015 Marin et al., 2015 Saravanan et al., 2015 £ȱȱǯǰȱŘŖŗś 28-31 17±2 20 14 25.9±0.1 -
ȱ ȱȱȱŝǯŖȱȱŝǯŚǯȱȱęȱ ȱ ȱ¢ȱǻȱȱǼȱȱȱȱ ȱȱȱȱȱȱŚǯśȱȱȱ ȱȱȱȱȱŗƖȱȱ¢ȱǯȱ ȱȱęȱȱȱȱȱȱ various studies, and blood samples yielding ȱȱȱȱ¢ȱ ȱȱȱȱ ęȱȱȱȱȱȱȱ¡ȱ ǻȬȱǼǯȱȱ ȱȱ ¢ȱ by heart puncture with heparinized needles ȱȱȱ£ȱȱǼǯȱ The studies were approved by the III Local ȱȱȱ ǯȱȱŗśŖȱΐȱ ȱȱ ȱȱȱȱęǰȱȱȱȱȱȱřŖȱǯȱȱȱ blood were subjected to routine hematological analysis (Svobodova et al., 1991, with own ęǼǯȱ ȱǻ Ǽǰȱȱ concentration (Hb), erythrocyte count (RBC), mean cell volume (MCV), mean corpuscular hemoglobin concentration (MCHC), leukocyte
phagocytes (NBT) were evaluated. Calcula-
0.90-0.98 0.79±0.15 1.49±0.12 1.47±0.20 1.14-1.46 0.76±0.03 0.83±2.35
230.0±37.9 176.6±13.5 236.8-268.8 191.4±11.1 285.8±78.5
hemoglobin (MCH), and mean corpuscular
34.1-55.6 114.3±4.4 76.6±7.6 102.5±8.0 56.4-69.0 49.2±2.7 78±22
51.0±7.5 243±29 78.8±10.0 446±44 47.1-49.5 183-200 65.0±3.5 340±20 91±31 -
18.2-20.6 197.3±6.3 36.0±4.4 43.8±6.8 61.2-62.3 30.4±1.3 41.5±5.0
5-6 11.3±0.1 46.3±7.7 80±5 25-45 5.8±0.8 10-15
ǻŘŖȬřŖȱǯǼȱȱȱęȱ ȱǰȱ
14.0±3.4 34.2±5.7 24±1 30.6-34.6 14.5±0.9 18±9.1
Age/mass Water Author ȱęȱǽǾ temp. [°C] WBC [103/μL] MCH MCHC [pg] [g/L] MCV [fL] Hb [g/L] RBC [103/μL] Ht [%]
Table 1.ȱǯȱȱȱǻƹǯǯǼȱȱȱȱȱȱȱCyprinus carpio (according to various authors).
ȱȱȱ¡¢ȱȱ ȱŝǯŖȬşǯŚȱȦǯȱ ȱȱȱȱȱŖǯřȱ ȱŗǯŖȱȦǰȱȱȱȱȱŖǯŖȱȱŖǯřȱȦǯȱ
count (WBC), thrombocyte count (PLT) and ȱ¡ȱȱ¢ȱȱ ȱȱ¢ȱ¢ǰȱȱěȱ ¢ȱȱǻȱȱ¢¢ǰȱ ȱȱ¢Ǽȱ ȱȱ ȱȱȱȱ ȱ¢ȱ ȱ and Giemsa solutions (300 erythrocytes and 100 ¢ȱ ȱ ȱȱęȱȱȱ Ǽǯȱęȱȱ¢ȱȱ¢ȱ ȱȱȱȱȱ et al. (1994). For Ht evaluation heparinized ȱ ȱȱ ȱȱȱŗŘǰŖŖŖȱ
Bull. Eur. Ass. Fish Pathol., 36(4) 2016, 173
ȱȱśȱȱȱȱȱȱȱȱ erythrocyte layer in entire blood volume was measured using a Ht reader. Hb was measured
ȱȱŗŖȱ ȱǻǰȱǼǯȱȱ ȱȱ¢ȱȱȱ ȱ
using spectrophotometric cyanmethemoglobin
and descriptive statistics were calculated:
DZȱŗŖȱΐȱȱȱ ȱ¡ȱ ȱŗȱȱ ȱȱǰȱ¡ȱ ȱȱȱśŚŖȱ nm wavelength, and hemoglobin concentration
ȱǰȱȱȱȱȱǰȱ
ȱȱȱȱȱȱȱ
ȱȱȱȱȱȱȱ
ȱȱ¡ȱȱȱȱ
to mean (in percent). For the literature data
standard hemoglobin solutions. For RBC and WBC counts blood was diluted 100 times with
the same parameters were calculated (n is the
Hayem’s solution, and the cells were counted in ȱ¢ȱȱƼŚŖŖȱętion. MCV, MCH, and MCHC were calculated
Ĝȱ ȱȱȱȱȱ ȱȱȱȱȱ
using Ht, RBC and Hb values according to the
¢ȱȱǻȱǂŖǯŖśǼǯȱ
ȱȱȬȱȱǻȱǂŖǯŖśǼȱ
standard deviation, median, minimum and ¡ǯȱĜȱȱȱ ȱȱ
ȱȱȱǼǯȱȂȱȱ
ȱȱ ȱȱȱęȱ
DZȱƽǻ ƼŗŖǼȦǰȱ ƽ Ȧǰȱ ƽǻ ƼŗŖŖǼȦ ǯȱ¢ȱȱǻǼȱ ȱȱȱȱȱȱ¢ȱ
Results and discussion
per 100 leukocytes in blood smears and WBC
mal distributions and the obtained ranges
values. Spontaneous oxidative metabolic activ-
ǻȬ¡Ǽȱ ȱ ȱȱȱęȬȬ
¢ȱȱ¢ȱ ȱȱȱȱ Siwicki et al. (1985) using the nitrotetrazolium ȱǻǼȱȱDZȱśŖȱΐȱȱȱ ȱ ȱ ȱȱȱȱȱŖǯŘƖȱȱ ȱȱȱȱŗȱȱȱŘŞǚȱǻ¡ȱ
ęȱ¢ȱǻȱŘǼǯȱȱȱȱ ȱȱȱȱȱȱǻ ǰȱǰȱ Hb, MCV and MCH) were slightly lower, while
¢ȱŗśȱǼǰȱȱŗȱȱȱ¢-
authors (Table 2b), which might have resulted
mide (DMF) was added to kill the cells and the
ȱȱǼǯȱ¡ȱ ȱȱȱśŚŜȱ
ȱȱȱȱȱȱęȱ ȱȱ ȱȱȱȱȱ ȱ¢ȱ¢ȱ ȱȱȱȱȱȱȱ ¢ǯȱȱȱȱȱȱ¢ȱȱ
nm wavelength using the spectrophotometer,
lymphocytes in our own studies were higher,
ȱ£ȱȱ ȱȱ
ȱȱȱȱ¢ȱ ȱ ȱ
ȱȱȱȱȱ ȱȱ ȱȱȱȱȱ-
ȱȱȱȱȱȱȱ studies. However, some authors reported ex-
mazan solutions.
tremely low WBC values (below 103ȦΐǼǯȱ ȱ
ȱ ȱȱȱśȱȱȱȱȱ ȱȱȱ£ȱǻȱȱ
ȱȱȱȱȱ ȱȬ-
MCHC was slightly higher compared to those ȱȱȱȱȱ¢ȱȱ
ěȱȱȱȱȱȱȱ ȱȱȱȱȱȱȱ
ěȱȱȱ¢ȱǰȱǯǯȱ
ȱȱǻǼȱ ȱěDZȱȱŚŗȱ ȱ¢ȱ¢ȱȱŗŚŜȱȱǯȱȱ
ȱȱ¢ȱȱǯȱ¢ȱȱ ȱȱȱȱȱȱ
results were subjected to statistical analysis
ȱǻśŖȱǼȱ ȱȱřŚƖȱȱȱ
174, Bull. Eur. Ass. Fish Pathol., 36(4) 2016
ȱȱȱ ȱȱȱȱ¢ȱ ǰȱŘŖƖȱȱĴȬ ȂȱǰȱŗŚƖȱ
ȱȱ¢ȱ¢ȱȱȱȱ ȱȱȱȱǰȱȱȱȱ
Prochazka-Skrobak’s,10% Dacie’s, 8% Turk’s,
ǯȱȱȱȱ¢ȱȱȱ
4% Rees-Ecker’s or Shaw’s, Marcano’s, Giemsa
ȱȱ¢ȱȱȱȱȱ
or PBS – each used by 2%. One author (2%) used
ȱǯȱȱȱ¢¢ǰȱ
ȱȱȱȱȱ¢ȱ in smear. Two authors (4%) used automated
neutrophils and monocytes reported by other authors were 50.4-95.9%, 0.8- 28.0% and 0.5%
methods, remaining 94% - manual count in
-13.6%, respectively (Table 1).
Burker or Neubauer hemocytometers. AccordȱȱȬȱȱǯȱǻŘŖŖŘǼǰȱĴȬ Ȃȱ
ȱ¡ȱȱ¢ȱȱ
ȱĜ¢ȱȱ¢ȱȱ
phagocytes obtained in the present study was
the WBC value obtained using this diluent was ę¢ȱ ȱȱȱȱȱ-
similar to that reported by Yonar (2013) and Yonar et al. (2014) (1.04±0.10 and 0.98±0.11
tained using indirect methods. Additionally,
Ȧǰȱ¢Ǽȱȱȱȱȱ£ȱȱ
the authors pointed out that this solution also
acclimated in a similar way to the laborato-
ȱ¢ǰȱ¢ȱȱȱ
ry conditions in this study. It was, however,
immature erythrocytes. Our own experiences with Turk’s and Shaw’s solutions revealed that all blood cell nuclei stained which made ȱ¢ȱ¢ȱĜȱȱȱȱ similarity to erythrocyte nuclei and thrombo-
ȱȱȱȱȱȱȱ ȱȱ¢ȱȱǻŗşşŜǼȱǻŗǯŜŘƹŖǯŜŖȱȦǼȱ
¢ǯȱǰȱ ȱȱ ¢Ȃȱȱ ǻȱȱ¢Ǽȱȱȱȱȱȱ
without any laboratory acclimation period. The ěȱȱȱȱ¢ȱ-
counts. Leukocytes were clearly visible as small
ditions this parameter may decrease, probably
ȱǰȱ¢ȱȱȱȱ
ȱȱ ȱȱȱ¢ȱȱȱȱ
erythrocytes and small oblong thrombocytes.
ǯȱȱȱȱȱȱȱȱ
Tavares-Dias et al. (2002) also compared the
ȱȱȱ¢ȱȱȱ optimum water quality.
Ĝȱȱȱȱȱȱtained by various authors and revealed that
ȱ ȱȱǯȱǻŗşŞśǼȱǻŗǯŞŖƹŖǯŘŖȱȦǼǯȱȱȱ studies analyses were carried out immediately ȱȱȱęȱȱȱȱǰȱ
ȱȱȱȱŞǯŖȱȱśŖƖǯȱȱȱ¢ȱ
¢ȱȱȱęȱȱ¢ȱ-
this value was 49%, while pooled data obtained
ȱȱȱȱȱȱęȱȱ
ȱȱȱ¢ȱȱȱǻȱŘǼȱ
one group with leukocytes due to considerable
showed 104%.
morphological similarity. Our data showed that ȱȱȱȱȱȱȱȱ¢ȱ
ȱȱȱȱȱ¢¢ȱ
variable. According to other authors mean PLT
(almost exclusively resting cells were observed,
ȱȱȱȱ¢ȱȱȱŖǯşƼȱŗŖ3Ȧ
ǻȱŗǼȱȱ ȱȱȱȱǻȱ
ΐȱȱŚŝǯŚȱƼȱŗŖ3ȦΐȱǻȱŗǼǯȱȱęȱȱ
1b) and monocytes (Figure 1c) in our study might have been related to very good health
ȱȱȱ¢DZȱȱȱ ȱ¢ȱȱǻȱŗǼǰȱȱ ǻȱŗǼǰȱȱȱȱǻȱŗǼǯ
ȱȱȱęȱȮȱ¢ȱ¡ȱȱ
Ht [%] RBC [106ȦΐǾ
ȱǽȦǾ ȱǽǾ MCH [pg] ȱǽȦǾ Erythroblasts [%] WBC [103ȦΐǾ Lymphocytes [%] Neutrophils [%] Monocytes [%] ȱǽȦǾ PLT [103ȦΐǾ
Parameter
140 146 143 119 122 116 41 134 51 51 51 122 50
# of ę 24.8±0.4 1.43±0.04 66.0±1.8 189.4±5.4 50.2±1.5 270.8±7.1 3.1±0.5 56.0±2.4 89.5±1.1 7.2±0.8 1.4±0.3 1.01±0.05 19.9±2.7
Mean ±SEM 4.5 0.47 21.8 59.2 16.1 76.8 3.1 27.7 7.7 6.0 2.4 0.57 19.4
S.D.
2a
25.0 1.31 65.0 178.7 48.0 278.3 1.0 52.3 92.0 6.0 0.8 0.93 13.2
Median 12.0-36.5 0.61-2.80 22.6-170.0 91.4-379.7 13.7-94.0 80.8-547.9 0.0-9.1 11.0-178.8 58.0-98.3 1.0-34.0 0.0-11.0 0.41-2.50 2.9-115.0
Ȭ¡ȱ
Mean ±SEM
34 29.0±1.5 35 1.49±0.10 34 73.8±3.5 24 227.7±13.6 22 59.8±5.9 23 245.7±15.5 34 42.5±7.6 10 80.2±4.3 10 10.4±3.0 8 3.7±1.6 4 14.2±11.1
# of studies 8.7 0.59 20.5 66.6 27.4 74.2 44.4 13.5 9.5 4.4 22.2
S.D.
2b
30.2 1.49 73.0 216.9 52.4 243.0 31.6 82.7 9.7 2.0 4.3
Median
13.7-43.6 0.33-2.95 37.6-114.3 130.9-412.7 31.8-139.0 120.0-446.0 1.4-197.3 50.4-95.9 0.4-28.0 0.5-13.6 0.9-47.4
Ȭ¡ȱ
Table 2.ȱ ȱȱȱśȬŞȱȱȱCyprinus carpioȱȱȱȱȱȱǯȬǯȱȱȱȱřȬŚȱ ȱȱȱ¢ȱȱǻŘǰȱǼǰȱȱȱȱȱȱȱCyprinus carpio by various authors listed in table 1 (2b, right).
Bull. Eur. Ass. Fish Pathol., 36(4) 2016, 175
176, Bull. Eur. Ass. Fish Pathol., 36(4) 2016
Figure 1.ȱ¢ȱȱ¢ȱȱȱȱȱǻȱȮȱ¢¢ǰȱȱȮȱ¢ǰȱȱȮȱ neutrophil, T – thrombocyte).
ȱȱȱȱȱȱȱȱ
ȱęȱȱ ȱȱȱ
ȱȱǰȱȱ ȱȱȱ-
ȱȱȱȱęȱ¢ȱ
ported by other authors (Table 2b), probably
ȱȱ ȱǰȱ¡ȱȱ ȱ
Ěȱȱ ȱȱȱęȱǰȱ£ǰȱ ȱ¢ǰȱǰȱȱȱ ȱ
negative relationships between MCV and body ȱǻƽȬŖǯŚŘǼǰȱȱ ȱȱȱ ȱ
¢ǯȱȱȱȱȱȱ ȱ
ȱǻƽȬŖǯŚřǼǯȱ
Bull. Eur. Ass. Fish Pathol., 36(4) 2016, 177
ȱȱȱȱȱȱȱęȱ ȱȱȮȱ ȱŘśȱȱśŖƖȱǻȱ
ȱȱȱȱęȱȱȱȱȱ£ǰȱ reared under similar environmental conditions
ǰȱ ǰȱǰȱ ǰȱ ȱȱǼǰȱȱ ȱȱǻȱȱ¢ǰȱ
ȱȱȱȱȱǯȱȱȱ
neutrophils and monocytes, PLT and NBT)
ȱȱȱȱȱ¢ȱȱśȬŞȱ month old juvenile common carp harvested in
they were high – over 50%, while low variation ǻ ȱŘśƖǼȱ ȱȱ¢ȱȱȱȱ ȱȱ
ȱȱȱȱȱȱ ȱȱ¢ȱȱȱřȬŚȱ ȱȱ
ȱȱ¢¢ǯȱȱȱȱ
ŗŜȬŗŞǚȱȱȱȱȱȱȱȱ
ȱĜȱ ȱȱȱȱȱ
ȱȱȱ¡ȱȱȱȱęȱ
ȱȱDZȱȱȮȱ ȱŘśȱȱśŖƖȱ
under similar conditions.
ȱ ǰȱǰȱ ǰȱǰȱ ȱȱ ǰȱȱ ǻȱśŖƖǼȱȱȱȱȱȱ monocytes, WBC and PLT, while low only in the
Acknowledgements
ȱȱȱȱ¢¢ǯȱȱ
ȱ¢ȱȱȱ¢ȱȱȱ ȱȱ ǰȱȱȱřŞŝȦŗŚȦǯ
ȱȱĜȱȱȱȱȱȱȱȱȱȱȱȱ ȱȱȱȱȱǻ ǰȱ¢ȱȱ lymphocytes), some moderately variable (RBC, Hb, MCV, MCH and MCHC), and some are ¢ȱȱǻ¢ȱȱȱȱ monocytes and PLT). According to Vosyliene ǻŗşşşǼǰȱȱȱȱȱȱȱȱȱ ęȱȱ¢ȱȬȱȱȱȱȱȱȱ¢ȱ ȱȱȱǯ The obtained results and their comparison with ȱȱȱȱȱȱ ȱ ȱ ȱ ȱ ¢ȱ Ĝȱ ȱ ȱ ȱ ȱȱȱȱǯȱ ȱȱȱ ȱȱȱȱęȱȱ natural environment to the laboratory inevitably ȱȱȱȱȱȱȱȱȱęǰȱȱȱȱ acclimation takes place and optimum water ¢ȱȱǯȱǰȱȱȱȱ ȱȱȱęȱȱȱ laboratory conditions and those sampled di¢ȱȱȱȱ¢ȱěǯȱ It is, however, possible to develop the ranges
ȱȱ¢ȱ ȱęȱȱȱ
References Ahmad SM, Shah FA, Bhat FA, Bhat JIA and Balkhi MH (2011). Thermal adaptability and disease association in common carp (Cyprinus carpio communis) acclimated to ěȱǻǼȱǯȱJournal of Thermal Biology 36, 492-497. ȱ ȱȱȱȱǻŘŖŗŖǼǯȱěȱȱ chronic copper exposure on haematology ȱ¢ȱȱȱȱǻCyprinus carpio L.). Journal of Applied Sciences and Environmental Management 14, 39-45. ȱ ȱ ȱǻŘŖŗŗǼǯȱȱȱȱǻǼȱȱ hematological parameters and behavioral changes in Cyprinus carpio (common carp). African Journal of Biotechnology 10, 1386013866. Al-Rudainy AJ and Kadhim MH (2012).
ȱȱ¡ȱěȱȱ ȱ ȱ ȱ ȱ ȱ Cyprinus carpio. The Iraqi Journal of Veterinary Medicine 36, 58-67. Ambayya A, Su AT, Osman NH, Nik-Samsudin NR, Khalid K, Chang KM, Sathar J, Rajasuriar JS and Yegappan S (2014).
ȱȱȱȱȱ multiethnic population. Plos One 9(3), 1-7.
178, Bull. Eur. Ass. Fish Pathol., 36(4) 2016 Bastami KD, Moradlou AH, Zaragabadi AM., Mir SVS and Shakiba MM (2009). ȱ ȱ ȱ ȱ ȱȱȱ ȱǯȱComparative Clinical Pathology 18, 321-323. Bojarski B, Ludwikowska A, Kurek A, Pawlak K, Tombarkiewicz B and Lutnicka H (2015). Hematological alterations in common carp (Cyprinus carpio L.) exposed to herbicides: ȱȱȱȱ separately and in mixture. FoliaBiologica (Kraków) 63, 167-174. Enache I, Cristea V, Docan A, and Popescu ȱ ǻŘŖŗŗǼǯȱ ȱ ȱ ȱ juvenile carp reared under a recirculating system condition. Aquaculture, Aquarium, Conservation & Legislation International ȱȱȱĚ¡ȱ¢ 4, 644-650. Ȭ¢ȱ ǰȱ ȱ ǰȱ ȱ ȱȱ ȱȱǻŘŖŗřǼǯȱěȱ ¢ȬȱCyprinus carpioDZȱȱȱ¢ȱ activity, hematological responses and serum biochemical parameters. Ecotoxicology and Environmental Safety 98, 35–141. Gul A, Benli ACK, Ayhan A, Memmi BK, Selvi M, Sepici-Dincel A, Cakirogullari GC and Erkoc F (2012). Sublethal propoxur toxicity to juvenile common carp (Cyprinus carpio L., 1758): biochemical, hematological, ǰȱȱ¡¢ȱěǯȱ Environmental Toxicology and Chemistry 31, 2085–2092. Gupta K, Sachar A and Raina S (2013). Seasonal ȱȱȱȱȱ Golden Mahseer, Tor putitora. International ȱȱęȱȱȱ 3, 895-898. Harikrishnan RM, Rani N and Balasundaram C (2003). Hematological and biochemical parameters in common carp, Cyprinus carpioǰȱ ȱ ȱ ȱ ȱ Aeromonas hydrophilaȱǯȱAquaculture 221, 41-50. Hrubec TC, Smith SA and Robertson JL (2001). Age-related changes in hematology and
ȱ¢ȱȱȱ¢ȱȱ ȱǻȱ¢ȱƼȱȱ¡Ǽǯȱ Veterinary Clinical Pathology 30, 8-15. Jagruthi C, Yogeshwari G, Anbazahan SM, Shanthi Mari LS, Arockiaraj J and ȱ ȱ ǻŘŖŗŚǼǯȱ ěȱ ȱ ¢ȱ astaxanthin against Aeromonas hydrophila ȱȱȱǰȱCyprinus carpio. ȱǭȱęȱ¢ 41, 674-680. Jahanbakhshi A, Hedayati A, Harsij M and Barkhordar M (2014). Hematological and ȱȱȱȱȱ Cyprinus carpioȱȱȱȱȱȱ oil. Comparative Clinical Pathology 23, 799– 803.
ȱ ȱ ȱ ȱ ȱ ǻŘŖŖŖǼǯȱ ȱ ȱ ȱ ȱ ȱ ȱ ȱ (Cyprinus carpioȱ ǯǼȱ ȱ Ěȱ ȱ natural population cyanobacterial water blooms. Acta Veterinaria Brno 69, 131-137.
ȱ ǰȱęȱǰȱ ȱǰȱ¢ȱ ȱȱȱ ȱǻŘŖŗŚǼǯȱěȱȱ¢ȱ b-(1,3)(1,6)-D-glucan supplementation on ȱǰȱȱ¢ȱ ȱ Ȭȱ ęȱ ȱ mirror carp (Cyprinus carpio L.). Journal of Animal Physiology and Animal Nutrition 98, 279–289. Kumar V, Makkar HPS, Amselgruber W and Becker K (2010). Physiological, haematological and histopathological responses in common carp (Cyprinus carpioȱǯǼȱęȱȱ ȱě¢ȱ ¡ęȱJatropha curcas kernel meal. Food and Chemical Toxicology 48, 2063-2072. Langer S, Sharma J and Kant KR (2013). Seasonal variations in haematological ȱȱȱȱęǰȱGarra gotyla gotylaȱȱ ȱȱȱ ȱǰȱ India. International Journal of Fisheries and Aquaculture Sciences 3, 63-70. Leard AT, Wagner BA, Camp KL, Wise DJ ȱ ȱ ȱ ǻŗşşŞǼǯȱ ȱ ȱ ȱ ȱȱȱȱȬȱ ȱ ęȱ ǻIctalurus punctatus) in the Mississippi Delta. Journal of Veterinary
Bull. Eur. Ass. Fish Pathol., 36(4) 2016, 179 Diagnostic Investigation 10, 344-349. Lehmann J, Hamers R and Sturenberg F-J (1994).
ȱȱȱǻCyprinus carpio ǯǼǯȱȱǯȱȱȬ ǰȱŝŖȱǯ ȱ ȱ ǻŗşşśǼǯȱ ȱ ȱ ȱ methods on the physiological normal values ȱȱȱȱȱęǯȱ Zivocisna Vyroba 40, 301-306. Luskova V (1997). Annual cycles and normal ȱ ȱ ȱ ȱ ȱ ǯȱ Acta Scientiarum Naturalium Academiae Scientiarum Bohemicae Brno 31, 1-70. Marin M, Nicolae C, Dragotoiu D, Urdes L, Raducuta I and Dinita G (2015). Researches ȱȱȱęȱȱ juvenile Cyprinus carpio varieties. ęȱ Papers Series D Animal Science 58, 209-212 ȱ ȱ ȱ ȱ ȱ ǻŘŖŗřǼǯȱ ȱ ȱ Cypermethrin on some hematological ȱȱȱȱȱ¢ȱ ȱȱ ȱǰȱCyprinus carpio. African Journal of Environmental Science and Technology 7, 852-856. Mikula P, Modra H, Nemethova D, Groch ȱ ȱ ȱ ȱ ǻŘŖŖŞǼǯȱ ěȱ ȱ subchronic exposure to LASSO MTX ǻȱ ŚŘƖȱ ȦǼȱ ȱ ȱ ȱȱ¢ȱȱȱȱǰȱ Cyprinus carpio L. Bulletin of Environmental Contamination and Toxicology 81, 475-479. Morgan AL, Thompson KD, Auchinachie ȱȱȱ ȱǻŘŖŖŞǼǯȱȱěȱȱ seasonality on normal haematological and ȱȱȱȱ ȱȱ Oncorhynchus mykiss L. ȱ ǭȱ ęȱ Immunology 25, 791- 799. Orun I and Erdemli AU (2002). A study on ȱȱȱȱĴ (Heckel, 1843). International Journal of Biological Sciences 2, 508-511. Pakravan S, Hajimoradloo A and Ghorbani ȱ ǻŘŖŗŘǼǯȱ ěȱ ȱ ¢ȱ ȱ ǰȱ Epilobium hirsutum extract on growth
ǰȱ ¢ȱ ǰȱ haematological parameters and Aeromonas hydrophila challenge on common carp, Cyprinus carpio. Aquaculture Research 43, 861–869. ȱ ǰȱ ȱǰȱȱ ȱǰȱěȱ J, Sodikromo J, Spaans M, Brouwer R, de Lathouder S and Hinzmann R (2010).
¢ȱ ȱ ȱ ȱ established and novel parameters in healthy adults. Sysmex Journal International 20(1), 1-9. Saravanan M, Karthika S, Malarvizhi A and Ramesh M (2011). Ecotoxicological ȱȱęȱȱȱȱȱ common carp (Cyprinus carpioǼȱęDZȱ Hematological, biochemical, ionoregulatory and enzymological responses. Journal of Hazardous Materials 195, 188– 194. Saravanan M, Kim J-Y, Kim H-N, Kim S-B, Ko D-H and Hur J-H (2015). Ecotoxicological ȱȱȱȱ ȱ ęȱCyprinus carpioȱęDZȱȱȬ biomarker assessment. Journal of the Korean Society for Applied Biological Chemistry 58, 491–499. £ȱǰȱ ȱ ȱȱ ȱȱǻŘŖŗśǼǯȱ ěȱȱȱȱȱĚȱǻŘǼȱȱ ȱȱȱȱȱȱ ȱȱȱǰȱCyprinus carpio ǯǰȱęǯȱArchive of Polish Fisheries 23, 107-111. Siwicki AK, Studnicka M and Ryka B (1985). ¢ȱ¢ȱȱȱȱȱ (Cyprinus carpio L.). The Israeli Journal of Aquaculture-Bamidgeh 37, 123-128. Úȱǰȱ ȱȱȱ£ȱ ȱǻŘŖŖŖǼǯȱ Ěȱȱ ȱȱ ȱȱ ȱȱȱȱȱęǯȱMedycyna Weterynaryjna 56, 593-597 [In Polish] ȱ ȱ ǻŗşşŜǼǯȱ ȱ ¢ȱ ȱ neutrophilic granulocytes in normal carps (Cyprinus carpio L.). Medycyna Weterynaryjna 52, 529-531. ȱǰȱÙȱǰȱ£ȬÙȱȱȱ Wiktorowicz K (2001). Cytometric analysis
180, Bull. Eur. Ass. Fish Pathol., 36(4) 2016 ȱȱȱȱȱ¡¢ȱȱȱ ȱ¢ȱȱ¢ȱȱ (Cyprinus carpio). Medycyna Weterynaryjna 57, 832-835. Sudova E, Piackova V, Kroupova H, Pijacek ȱȱȱȱǻŘŖŖşǼǯȱȱěȱȱ praziquantel applied per os on selected haematological and biochemical indices in common carp (Cyprinus carpio L.). Fish Physiology and Biochemistry 35, 599–605. ȱǰȱȱǰȱȱǰȱȱȱ and Fijan N (2002). Haematology and some ȱȱȱȱ¢ȱȱ ȱȱȱȱȱ¢ǯȱActa Veterinaria Hungarica 50, 459-467. Svobodova Z, Pravda D and Palackova J ǻŗşşŗǼǯȱęȱȱȱȱ ¡ȱ ȱ ęǯȱ ȱ ǯȱ ŘŖǯȱ ȱ ȱ ȱ ȱ ȱ ȱ Hydrobiology, Czech Republic. Tavares-Dias M, Mataqueiro MI and Perecin ȱǻŘŖŖŘǼǯȱȱ¢ȱȱȱęȱ by direct or indirect methods? Boletim do Instituto de Pesca 28, 155-161. Thangam Y, Jayaprakash S and Perumayee ȱ ǻŘŖŗŚǼǯȱ ěȱ ȱ ȱ ¡¢ȱ ȱ ȱȱȱȱ ȱ ęȱCyprinus carpio (common carp). IOSR Journal of Environmental Science, Toxicology and Food Technology 8, 50-60. Tripathi NK, Latimer KS and Burnley VV ǻŘŖŖŚǼǯȱ ȱ ȱ ȱ ȱǯ (Cyprinus carpio), including blood cell morphology, cytochemistry, and ultrastructure. Veterinary Clinical Pathology 33, 74-83. Velisek J, Svobodova Z and Machova J (2009). ěȱȱȱȱȱǰȱ biochemical and histopathological ȱ ȱ ȱ ȱ ǻCyprinus carpio L.). Fish Physiology and Biochemistry 35, 583–590. Velisek J, Sudova E, Machova J and Svobodova ȱǻŘŖŗŖǼǯȱěȱȱȬȱ¡ȱȱ
terbutryn in common carp (Cyprinus carpio L.). Ecotoxicology and Environmental Safety 73, 384–390. Velisek J, Stara A, Machova J and Svobodova ȱǻŘŖŗŘǼǯȱěȱȱȬȱ¡ȱȱ simazine in real concentrations on common carp (Cyprinus carpio L.). Ecotoxicology and Environmental Safety 76, 79–86. ¢ȱȱǻŗşşşǼǯȱȱěȱȱ¢ȱȱ ¡ȱ ȱ ȱ ȱ ȱ ȱ ǯȱ ¢ȱ ȱ ȱ environment. An integrated approach. D.A. Lovejoy (Ed.) 295-298pp.’ Wang X-F, Li X-Q, Leng X-J, Shan L-L, Zhao ȬȱȱȱȬȱǻŘŖŗŚǼǯȱěȱȱ¢ȱ Ĵȱ ȱ ȱ ȱ ȱ ǰȱ hematological indices, liver and gonad ¢ȱȱȱȱȱǻCyprinus carpio). Aquaculture 428–429, 79–87. Wlasow T and Dabrowska H (1990). Hematology ȱȱȱȱ¡ȱ ȱǯȱ Polskie Archiwum Hydrobiologii 37, 419–428. £ȱ ȱ ǻŗşşŞǼǯȱ ěȱ ȱ ¡ȱ ȱ ȱȱĚȱȱ ěȱȱȱȱȱǻCyprinus carpio L.). The Israeli Journal of AquacultureBamidgeh 50, 82-85. ȱȱǻŘŖŗřǼǯȱ¡ȱěȱȱȱȱ carp, Cyprinus carpio carpio: Protective role ȱ¢ǯȱEcotoxicology and Environmental Safety 97, 223–229. Yonar SM, Ural MS, Silici S and Yonar ME (2014). Malathion-induced changes in ȱȱęǰȱȱȱ ǰȱȱȱ¡Ȧ¡ȱ ȱȱCyprinus carpio carpio: Protective ȱ ȱ ǯȱ Ecotoxicology and Environmental Safety 102, 202–209.