(KHV) from Potential Vector Species to Common Carp
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212, Bull. Eur. Ass. Fish Pathol., 32(6) 2012 Horizontal transmission of koi herpes virus (KHV) from potential vector species to common carp J. Kempter1ǰȱǯȱ ÙÚ1, R. Panicz1*, J. Sadowski1, ǯȱ¢Ù 1 and S. M. Bergmann2 ŗȱȱȱǰȱ¢ȱȱȱȱȱǰȱȱȱ ¢ȱȱ¢ȱȱ££ǰȱ ££ȱ à £ȱŚǰȱŝŗȬśśŖȱ££DzȱŘȱȬ ĝȬ ȱǻ Ǽǰȱȱȱ ȱȱȱ ǰȱ ȱȱ ¢ȱȱ ǰȱûŗŖǰȱŗŝŚşřȱ Ȭȱ ȱǰȱ ¢ Abstract ¡ȱęȱǰȱęȱȱȱȱȱȱȱȱǻ Ǽȱǰȱ¢DZȱ ȱǰȱȱǰȱǰȱȱěǰȱȱȱȱȱȱ ȱȱȱ ȱ¢ǯȱȱęȱȱȱȱȱȱȱȱęȱȱ¢ȱ ȱ ȱȱ been diagnosed and prior to the beginning of the research study the presence of the virus genome ȱęȱȱȱȱęȱȱȱǯȱęȱȱȱǻǼȱȱ utilized in the experiment originated from the University of Wageningen. During a four-week period the SPF carp were exposed to infection through cohabitation with vector species previously ęȱȱ ȱǯȱȱȱȱȱȱ¢ȱȱȱ£ȱ- mission of KHV between selected species, even in the case of species showing no clinical signs of KHV disease (KHVD), while an average water temperature in the tanks ranged from 12°C to 16°C. Introduction Koi herpes virus (KHV) disease (KHVD) is a free) SPF common carp (Bergmann et al., 2010). serious viral disease causing mass mortality in The possibilities of the virus being transferred the species ¢ȱ. According to pre- ¢ȱęȱȱȱȱȱ ȱ¢ȱ vious research, clinical signs can be observed as part of an experimental study performed by not only in common carp (ǯȱ), but also Kempter et al. (2008). According to the results, in hybrids: ǯȱ x ȱ and ǯȱ during experimental infection by immersion, x ȱ. Immersion aquaria species such as tench (ȱ), vimba (ȱ challenge experiments, showed severe losses ), common bream (ȱ) and Ğȱȱ ȱ ȱȱȱ ȱ grass carp (¢ȱ) can transmit řśƖȱȱŗŖŖƖȱȱȱ¡ȱęȱȱȱ¡ȱȱ KHV to SPF carp when water temperatures ȱ¢ȱȱ ȱȱȱǻęȬȬ range between 18 and 27°C. The four potential * Corresponding author’s email: [email protected] Bull. Eur. Ass. Fish Pathol., 32(6) 2012, 213 ȱȱ ȱęȱȱȱ¢- River in south-western Poland (N50°45’14.364”, tomatic carriers of KHV by PCR analysis of gill E18°36’30.1068”). Koi herpes virus (KHV) was swabs prior to the start of the aquaria cohabita- ¢ȱęȱȱȱȱȱ- ȱ¡ǯȱȱȱ ȱęȱ tured common carp in 2004 (Bergmann et al., in SPF carp in samples of gill or pooled visceral 2006) and its presence was subsequently con- material (Kempter et al., 2008). Samples were ęȱȱ ȱȱǰȱȱȱ analysed according to methods summarised spring and summer of 2006 and 2007, prior in Table 1. In 2010, carp production in Poland ȱȱȱȱęȱȱȱȱȱȱ amounted to 15,400 tonnes per annum, and experiment in 2008. The following potential the estimated number of carp farms reported ȱęȱȱ ȱȱȱȱ as 500 (Lirski, 2011). Therefore, it would seem in experimental trials: common roach (ȱ advisable to analyze the risk connected with the ), European perch (ȱĚ), tench, ȱȱ¢ȱęȱȱȱ ȱěȱǻ ¢ȱ), silver carp ponds, as they may constitute a reservoir carp ( ¢¢ȱ¡) and grass of KHV infection without displaying the clinical ǯȱȱȱęȱ ȱȱȱ signs. The intention of this research study was the Fisheries Research Station (RSD) in Nowe ȱȱ ȱȱęȱȱȱ Czarnowo (March, 2008) in sealed bags with from carp might act as a vector introducing an appropriate amount of oxygenated pond ȱȱ¢ȱęȱǯ water. On arrival at RSD, they were placed in 1m3 ǰȱęȱ ȱȱ ȱȱŗŘȬŗŜ°C. Materials and methods During the four-week cohabitation period the Experimental infection tank water was neither replaced nor comple- Fish adjudged to have the potential to play a role ȱ ȱȱ ȱȱ ȱęȱ ȱȱȱȱȱĴȱ ȱȱ ȱ was not conducted. The potential vector species as being species that are important for angling intended for experimental infection were placed ȱęȱȱȱ ȱȱȱ ȱȱȱǻȱƽȱŘŖȱęȱȱǼȱȱ farms located in the catchment area of the Oder ȱ ȱęȬȬȱǻǼȱ ȱŗǯȱȱ£ȱȱȱȱęȱȱȱȱȱ ȱȱȱȱ¢ȱǯ Primer ȱǻśȂȬřȂǼ ȱ£ References KHV-F GACGACGCCGGAGACCTTGTG Gilad et al. 486 bp KHV-R CACAAGTTCAGTCTGTTCCTCAAC (2002) KHV-1Fn CTCGCCGAGCAGAGGAAGCGC Bergmann et al. 414 bp KHV-1Rn TCATGCTCTCCGAGGCCAGCGG (2006) KHV-TK-F GGGTTACCTGTACGAG Bercovier et al. 409 bp KHV-TK-R CACCCAGTAGATTATGC (2005) KHV-TK-Fn CGTCGTGAGGAATACGACG Unpublished Way 348 bp KHV-TK-Rn ACCGTACAGCTCGTACTGG (2007) 214, Bull. Eur. Ass. Fish Pathol., 32(6) 2012 common carp (n = 20 per tank) with a code second round of PCR was applied in case of line R8f10 xR3f10 obtained from the University of low copy numbers of virus genome. The PCR Wageningen (The Netherlands). The SPF carp products of KHV-F/KHV-R primers were used ȱ ȱȱęȱȱȱ¢ȱ as a template for a second nested PCR with ȱȱȱ ȱǯȱȱȱęȱ KHV-1Fn/KHV-1Rn primers (Gilad et al., 2002; species and SPF carp were of a comparable size, Bergmann et al., 2006). A second set of primers ¡¢ȱŗǯśǯȱȱȱȱęȱȱ comprised of KHV-TK-F/KHV-TK-R primers ȱ¡ȱǰȱŘŖȱęȱȱȱȱ ȱȱęȱȱȱ Ȭ ȬȦ Ȭ Ȭȱ were screened for KHV. DNA was extracted applied in the nested PCR (Bercovier et al., 2005; using DNAzol (Invitrogen) reagent from liver, Way, 2007 [unpublished]). The PCR assays were intestine and pancreas and a standard diag- performed according to previously published nostic polymerase chain reaction (PCR) assay methods and the primers and methods used in according to published primers was applied this study are detailed in Table 1. (Bercovier et al., 2005). As expected, the SPF carp screened KHV negative, however, the In order to verify the presence and the correct ȱȱ ȱȱ ȱęȱȱ size of the PCR products, electrophoresis on tissue samples collected from all potential vector a 1.5% argarose gel (Prona), utilizing Power- species. A negative control group (n = 150) of Pack™ Basic (BioRad) was performed. The am- SPF common carp, code line R8f10 x R3f10, were plicons were visualized with the Gel Doc™XR maintained in spring water at 12-16 ºC. All tanks (BioRad) and sized according to a GeneRuler™ were physically separated from each other in 100 bp Plus DNA ladder (Fermentas). order to prevent cross contamination between experimental tanks. Results No mortality or clinical signs of KHV disease KHV detection ǻ Ǽȱ ȱȱȱ¢ȱȱȱęȱȱ Ğȱ¢ȱŝǰȱŗŚǰȱŘŗȱȱŘŞȱȱȱ¡ǰȱ constituting the reservoir of KHV nor SPF carp. 2 SPF carp were randomly selected from each The water temperatures recorded during the ex- tank and analysed by PCR in order to detect perimental trials ranged from 12-16°C, with an KHV DNA. Gill samples were aseptically col- average water temperature of 14°C during the 4 lected from each SPF carp (sample 1), as well as week cohabitation period. Detailed results are a fragment of the intestine, liver and pancreas summarised in Table 2. In the SPF carp used as a as an organ tissue pool (sample 2). negative control group, no KHVD clinical signs were observed and KHV DNA was not detected The collected tissues were homogenised with at any point during the experimental trial. KHV scissors and DNA was isolated according to DNA was detected from all carp sampled at 28 DNAzol (Invitrogen) reagent following manu- ¢ȱȱǻǼȱȱ ȱȱęȱ Ȃȱǯȱȱęȱȱȱ demonstrating any clinical signs consistent with presence or absence of the virus involved a ǯȱȱ¡ȱęȱȱ ȱ standard procedure of PCR and nested PCR ȱȱ£¢ȱĴȱ¢ȱȱ ȱȱȱȱ ȱęȱǯȱȱ ęȱȱęȱȱȱ ȱȱȱ¢ȱ Bull. Eur. Ass. Fish Pathol., 32(6) 2012, 215 ȱŘǯ KHV DNA detection using nested primers, Bergmann et al. (2006) and Unpublished Way (2007), Ğȱȱȱŝth, 14th , 21rst and 28th dp cohab. Variants ¢ȱŝ ¢ȱŗŚ ¢ȱŘŗ ¢ȱŘŞ ȱ¢ȱȱȱ ȱ ȱ¢ȱ ȱ Gills Pool Gills Pool Gills Pool Gills Pool SPF carp + Cr 3/4 nr 4/4 nr 4/4 4/4 nr nr SPF carp + Ep 4/4 nr 4/4 nr 4/4 4/4 nr nr SPF carp + T 2/4 nr nr nr 3/4 nr 1/4 nr SPF carp + Er nr nr 4/4 nr 2/4 nr nr nr SPF carp + Sc 2/4 nr nr nr 4/4 4/4 1/4 nr SPF carp + Gc nr nr nr nr 4/4 4/4 nr 4/4 SPF carp (k-) nr nr nr nr nr nr nr nr ȱ¢ȱȱȱ Ȭ ȱ ȱ¢ȱ Ȭ ȱ Gills Pool Gills Pool Gills Pool Gills Pool SPF carp + Cr nr 1/4 nr 4/4 nr nr 4/4 4/4 SPF carp + Ep nr 4/4 nr 4/4 nr nr 4/4 4/4 SPF carp + T nr 1/4 nr nr nr nr 1/4 4/4 SPF carp + Er nr nr nr nr nr 2/4 1/4 4/4 SPF carp + Sc nr nr nr nr nr nr 1/4 4/4 SPF carp + Gc nr nr nr nr nr nr 1/4 4/4 SPF carp (k-) nr nr nr nr nr nr nr nr ȱȬȱȱǰȱȱȬȱȱǰȱȱȮȱǰȱȱȬȱȱěǰȱȱȬȱȱǰȱ ȱȬȱ ȱǰȱ ǻȬǼȱȮȱȱǰȱęȱȱƸȦȱǰȱȱƽȱȱǯ ȱǯȱȱȱęȱȱȱ ȱȱȱȱȱȱęȱȱ in the study were able to transmit KHV DNA to for relay or re-stocking in natural waters and for naïve carp, in our case Dutch SPF carp. ęȱȱ¢ȱȱȱȱǯȱ Research conducted in order to create an epi- demiological map of the Oder catchment area In order to determine the epidemiological risk raises the question as to whether certain species connected with KHV, it is important to specify which are not considered to be typical KHV ¢ȱ ȱȱęȱȱ carriers, but whose carrier status have been ęȱȱȱǰȱ ȱȱȱ described, such as pike (¡ȱ), bullhead display KHVD clinical signs, may infect cypri- (Ĵȱ) or tench (ǯȱ), may take part ȱǯȱȱȱȱȱĞȱ in spreading the virus as a vector (Kempter et not representatives of the family Cyprinidae. al., 2008). The authors of this report previously 216, Bull. Eur. Ass. Fish Pathol., 32(6) 2012 ȱȱęȱȱȱȱȱ ȱȱȱ ȱȱę¢ȱǯȱȱ ȱǻȱřǼȱ ȱȱȱęȱȱ ȱȱȱȱȱęȱęȱȱȱ KHV carriers due to KHV DNA detection by carriers for all species sampled, the largest pro- ǯȱȱęȱȱȱȱ¢ȱ ȱȱ portion of carriers were Prussian carp (ȱ ȱęȱǰȱȱȱȱȱ ) (52.3%), common bream (40%), tench ȱȱȱǯȱȱȱęǰȱȱȱ (34%) and pike (20%).