Karin Boxaspen Institute ofmarine Research, Austevoll Aquaculture Research Station N Storeb0, Norway.

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ICES C.M. 1994 C.M.19941F:21 COMPARISON OF THE EFFECT OF DICHLORVOS AND PYRETHRINS AGAINST SALMON LICE (Lepeophtheirus salmonis) PARASITIC ON SALMON (Salmo salar) BY ONE OR SUCCESSIVE TREATMENTS. ABSTRACT Karin Boxaspen Institute ofmarine Research, Austevoll Aquaculture Research Station N- 5392 Storeb0, Norway. Experiments with a flower extract containing Pyrethrins generally used as an insecticide has been carried out at Austevoll Aquaculture Research Station since 1989. Different types ofadministration methods have been tested and in this report a bathexposure to the treatment solutionhas been used. Dichlorvos (Nuvan, Ciba Geigy) and Pyrethrins (Py-SaI25, Norsk Pyrethrum AIS) were tested, as a delousing agent successively one, two and then six times on individually tagged groups of salmon in the line with regular delousing. The delousing was done in accordance with the advises from the producers of the treatment solutions. The numbers of lice were registered between and after delousing. Delousing was carried out for both treatments at different times ofthe year to see if any difference in susceptibility to treatment was evident. Overall both treatments gave an adequate delousing effect measured by the decrease in total Iice numbers but the ongrowth of lice was more rapid in some of the dichlorvos groups. No certain difference in delousing capacity could be detected between the two treatment methods on mobile i"r ~ t 'lt Pyre~~lrir:.s3;;::-:-1 t() 1:.1.':,~ffect on H c eh:li 11.'. ':.~..; :

INTRODUCTION In Norway two species of ectoparasites usually referred to as salmon- or sea lice, Ure found on cultivated salmon (Salmo salar) with up to 100% prevalence. Tbey are both copepoda of the family Caligidae eating mucus, skin and blood oftheir host, thus creating lesions, osmoregulatory problems and secondary infections (Brandal et al., 1976; Wootten et al., 1982; Pike, 1989). Tbe predominating species in Norwegian waters is Lepeophtheirlls salmonis while Caliglls elongatzls so far occurs in smaher numbers and hence causes less damage. C. e!ongatus is not considered very host specific and has been reported on some 80 fish species (Kabatri, 1979, Johnson and Albright, 1991). L. salmonis, however, is believed to be host specific to salmonids. Bruno and Storie, (1990) reported findings of preadult L. salmonis on saithe (Po/lachills virens L.) kept elose to salmon cages but only C. elongatus was found on saithe kept in cages away froin salinon farms. No YOlmger stages of L. salmonis have been found on saithe and so far salmonids seem to be the only species were the louse can live their total life cycle. Tbe use of the term salmon lice is therefore identical with L. salmonis in this article. Tbc work on sea- and salmon lice at AustevoH Aquaculture Research Station started in 1987 and \vith fuh-time studies from 1989 with regular registrations oflice all year round. C. elongatlls have in this time become more regular and more numerous especially the last two years. However when delousing the cause is always large numbers ofl. salmonis. Salmon lice are recognised as one ofthe major loss factors in salmon farming today. Calculation of thc possible size ofthc loss to the industry varies but including chemicals for delousing, man hours for delousing, weight loss from stress, possiblc loss of fish and other thc sum approach about 500 mill NOK. (f. 50-60 inill) a year in Norway alone. Lice are also a major problem in other salmon producing countries like Ireland, Scotland and the Faroe Islands. So far only chemotherapeutic treatments have been available against salmon lice and the most used is dichlorvos in the form ofnuvan or Aquagard (both Ciba-Geigy) or thrichlorfon (Neguvon, Bayer) wich was introduced as the first method of chemical delousing by Brandal and Egidius, (1979). Both compounds are acetyl cholinesterase (AChE) inhibitors and as such nerve poisons (SaIte et al., 1987, Hoy et al., 1991).,Pyrethrum is an extract from a chry~anthemum flnwer (Chry"anthernum cinerariapjofill1n), 3r~wn commercially on the high plains of Kenya. Extrrictsfrorn this or re1ated plant species containing Pyrethrins as the active component have been used in insecticides by the industrialised world for more thari 150 years and the effect ofpyrethrum on mammals and environment is weh documented (e.g. Casida, 1973). In the autumn of 1989 a new administration principle for using Pyrethrins to combat sea lice \vas tested for the first time (Jakobsen and Holni, 1990, Boxaspen and Holm, 1991). Tbe experiment made use of Pyrethrum dissolved in oil instead of adding a synthetic emulsifier to make a water based Pyrethrum solution. The water solubility of the salmon mucus apparently leaves the fish unharmed while the salmon lice with a lipid membrane in the exoskeleton, are selectively penetrated. Pyrethrum was selected as a possible, candidate for improved chemotherapy because of the already existing legislation for usc in food industry (as an insecticide), the rapid breakdo\'.n (Maciver, 1962, Otieno & Pattenden, 1979) und the documented low rriaminalian toxicity (Barthel, 1973, Griffin, 1973). Thc retention time for salmon after treatment \vith thc commercial dclousing agent Py-Sal 25 containing Pyrethrins is set to 7 days by Norwegian Medicines Control Authority. '. I' "

MATERIALS AND METHODS All experiments were done at Austevoll Aquaculture Research Station on salmon held in sea eages and naturally infested with salmon lice. Chemieal eompounds: Dichlorvos was obtained as the commercial delousing agent Nuvan from Medisinaldepotet, Norway and Py-SaI25 containing pyrethrins, obtained from Norsk Pyrethrum AIS, Norway. Counting ofiiee: The salmon \vere anaesthetised by Metomidate (MaUson and Riple, 1989). This was done in to 100 I tanks depending on salmon numbers and size. The total numbers ofmobile lice were counted by visual registration in four groups, divided into grown and preadult ofboth sexes on individually tagged fish before treatment. The day after treatment the procedure for eounting was repeated to verify any delousing effect. Treatment proeedure: Nuvan After counting of lice the fish were revived with running water in a tank of 1 m3. The volume of sea \vater in the tank was then reduced to 800 1 and 2 ml of Nuvan was added. The fish were deloused in this solution under constant aeration for 40 minutes before running water washed out the treatment solution. Pyrethrins One litre of Py-Sal 25 mixture was placed into a small sink of 25 em x 15 cm x 5 cm and the anaesthetised fish was tumed for 4 to 6 seconds as ShO"ill in Fig. 1. Then the fish were revived in a tank of 1 m3 with running water similar to the fish in the Nuvan treatment..(j r; _.~..; Fig. 1 Principle for bath treatment with Pyrethrin solution.

Experimental design: The comparative treatments were done on a total of five groups of salmon. They were eighter treated one (I), two (11) or six times (III) successively. I: Single treatment. Parallel delousing with the two treatments were conducted as outlined in Table I for single treatments. Table I No. and size ofsalmon in single treatments. Time No. Pyrethrin group Size (cm±st.dev) No. Dichlorvos group Size (cm±st.dev) July 1991 21 (36.4 + 2.1) 28 (37.7 cm ±3.5) August 1991 February 1992 19 (28.9 ±,1.7) (28.6 cm ± 1.8) 11: Two successively treatments. From end of April to beginning of June 1991 the development of salmon lice on two groups of salmon taken from the same pen (each group containing 25 fish) were followed through two necessary delousings with dichlorvos and pyrethrins respectively. On Day 10 after 1st treatment an additional counting was done to establish the ongrowth oflice. 111: Six successively treatments. At 21 st of August 1992 two groups of Iice free salmon (each group containing 27 fish) were transferred to sea eages. From September same year to March 1993 they were followed through a total of six delousing proeedures. The fish were kept in separate sea eages throughout the experimental period thus getting naturally infested with lice. RESULTS AND DISCUSSION All results were compared with a Student's t-test for significanceofdifferences.... ~"' :.. " "'" -:,. ~... I All single treatments gave a significant decrease in lice numbers on the fish (Table 11). The Im.ver effect of delousing in February in both groups might be explained by the lower temperature.

Table 11 Lice numbers before and after single treatments with Pyrethrins or Dichlorvos given as total no. oflice (± st. dev). Time Pyrethrins start Pyrethrins end Delousing Dichlorvos (%) start Dichlorvos Delousing end (%) July 1991 69.6 (± 13.5) 1.5 (± 1.3) 97.8 66.1 (±12.9) 1.3 (± 1.2) 98.0 August 1991 19.8 (± 5.4) 3.5 (± 3.2) 82.3 23.2 (± 6.6) 1.7 (± 1.1) 92.7 February 1992 10.9 (± 5.2) 4.3 (± 3.7) 60.6 10.9 (± 5.2) 3.7 (± 2.1) 66.1 11 Delousing in both groups gave a significant decrease in numbers of lice (Fig. 2). Before the two delousings the lice numbers in the Dichlorvos group \vere significantly higher than in the Pyrethrin group (Pdich=0.02/p pyr =0.024) The day after treatment the opposite relationship were found (Pdich=0.024/p pyr =0.001).The Dichlorvos treatment thus gave a better delousing. At Day 10 after the first delousing the Pyrethrin group had a significantly lower count of lice (P=O.O 16) as was the case before the second delousing. Thus the ongrowth oflice in the Pyrethrin group was slower than in the Dichlorvos group. This effect can be explained by Pyrethrins affecting the chalimus stages of the lice and thus decimate the transition to pre- and adult lice. 80 OJ U.1"1 r-t \I- e 60 0 0 E r-t 0 co C,.Ul I;;j., w e.. 40 OlOJ ro c- e.. OJ > <t 20 1 ##,#,'" """", \ ".....,/,..,',,. - -, '....,,,' ""...... 1 7 14 May 21 June Date Fig. 2 Development oflice numbers with two successive treatments. De, marks date ofdelousing. ( Dichlorvos,...{)... Pyrethrins).

III All six points oftreatment for both groups offish gave significant delousing (Fig. 3). There was no difference in lice numbers when the treatments started but before delousing 2 and 4 the Dichlorvos group had a significantly higher number of lice. After delousing 2, 3, 4 and 6 the Pyrethrin had a significantly lower number of lice. This again indicates that Pyrethrins might affect the chalimus stages of the salmon lice. The settlement of copepodids on the fish come in pulses (pers.obs.) and copepodids settled after one of the points of treatment will make an even ongrowth in both groups. Chalimus already present on the fish will be exposed to the treatments and thus give an uneven pattern ofongrowth if influenced by the treatments. This seems to be the case after treatment 1, 3 and possibly 5 in the Pyrethrin group. This will be further studied. 100 90 80 Q.l u 'n 70 rl \I- C 0 0 60 E rl 0 cu 50 c (/) Q.l t... 40 C1Q.l cu n t... Q.l > «20 10 0 0 20 40 60 ~.E [. r.-,; 80 100 120 140 160 180 200 220 240 Days"'atter start Fig. 3 Development oflice numbers with six successive treatments. ( -e- Dichlorvos,..--0_. Pyrethrins). REFERENCES Barthel W.F., 1973, Toxicity of Pyrethrum and its constituents to mammals., in: Pyrethrum the natural insecticide, chap 6, p123-142, CasidaJ.E. (Ed.), Academic Press. Boxaspen K., and J.C. Holm. 1991. New bioeides used against sea lice compared to organophosphorous compounds, In N. De Pauw and J. Joyce (Eds),Aquaculture and the Environment, European Aquaculture Soc. Special Publication No. 16, Gent Belgium.

Brandal P.O., and E. Egidius. 1979. Treatment ofsalmon lice, (Lepeophtheirus salmonis, Kroyer 1838) with Neguvon - Description ofmethod and equipment. Aquaculture 18:183-188. Brandal P.O., E. Egidius & I Romslo, 1976, Host blood: a major food component for the parasitic copepod Lepeophtheirus salmonis Kmyer, 1838 (Crustacea:Caligidae), Norw. J ZooI., 24, 341-343. Bruno D.W., and J. Stone. 1990. The role of saithe, Pollachius virens L., as a host for the sea lice, Lepeophtheirus salmonis Kroyer and Caligus elongatus Nordmann. Aquaculture 89:201-207. Casida, E. (ed.) 1973, Pyrethrum, the natural insecticide. Academic Press, New York, London. 329p. Griffin C.S., 1973, Mammalian toxicity ofpyrethrum, Pyrethr. Post, 12(2),50-58. Hoy T., T.E. Horsberg, and R. Wichstrom. 1991. Inhibition of acetyl cholinesterase in rainbow trout following dichlorvos treatment at different water oxygen levels. Aquaculture 95:33-40. e Jakobsen P.J., and J.C. Holm. 1990. "Promising tests with new compound against salmon lice". Norsk Fiskeoppdrett 15(1):16-18. [In Norwegian]. Johnson S.C. and L.J. Albright, 1991, The developmental stages of Lepeophtheirus salmonis (Kroyer, 1837) (Copepoda:Caligidae), Can.J.Zool., 69, 929-950. ' Kabata Z., 1979. Parasitic Copepoda in British Fishes. The Ray Soc. No 152. London. Maciver, D. R., 1962, Preliminary experiments on the stability of pyrethrins in aqueous emulsions, Pyrethr. Post, 6(4),20-21. Mattson N. and T.B. Riple, 1989, Metomidate, a better anaesthetic for cod (Gadus morhua) In comparison with benzocaine, MS-222, chlorbutanol and phenoxyethanol, Aquaculture, 83, 89-94. Otieno D.A. & Pattenden G., 1979, Degradations ofnatural pyrethrins, Pyreth. Post, 15(2),-37. Pike, A.W., 12~9? SeaLice.-.Major P~thogens,oflaqned Atlantic Sal".l.qn,-P_arasitol~gy_Today~;5(9), 291-297.', SaIte R., M. Syvertsen, M. Kjonnoy, and F. Fonnum. 1987. Fatal acetyl cholinesterase inhibition in salmonids subjected to a routine organophosphate treatment. Aquaculture 61: 173-179. Wootten, R., J.W. Smith & E.A. Needham, 1982, Aspects ofthe biology ofthe parasitic copepods Lepeophtheirus salmonis and Caligus e!ongatus on farmed salmonids and their treatment., Proc.Roy.Soc.Edinburgh, 81 B, 185-197.