|Male and female Lepeophtheirus salmonis|
Burmeister, 1834 
A sea louse (plural sea lice), not to be confused with sea fleas, is a member of a family of copepods (small crustaceans) within the order Siphonostomatoida, family Caligidae. There are roughly 559 species in 37 genera include around 162 Lepeophtheirus and 268 Caligus species. Sea lice are marine ectoparasites (external parasites) that feed on the mucus, epidermal tissue, and blood of host marine fish.
This article focuses on the genera Lepeophtheirus and Caligus which parasitize marine fish, in particular those species that have been recorded on farmed salmon. Lepeophtheirus salmonis and various Caligus species are adapted to salt water and are major ectoparasites of farmed and wild Atlantic salmon. Several antiparasitic drugs have been developed for control purposes. Since L. salmonis is the major sea louse of concern and is the best understood in the areas of its biology and interactions with its salmon host, this review will focus on this species.
Caligus rogercresseyi has become a major parasite of concern on salmon farms in Chile, and studies are under way to gain a better understanding of the parasite and the host-parasite interactions. Recent evidence is also emerging that L. salmonis in the Atlantic has sufficient genetic differences from L. salmonis from the Pacific to suggest that Atlantic and Pacific L. salmonis may have independently co-evolved with Atlantic and Pacific salmonids, respectively.
- 1 Diversity
- 2 Wild fish
- 3 Morphology
- 4 Development
- 5 Feeding habits
- 6 Disease
- 7 Fish farming
- 8 Treatments
- 9 Other points of interest
- 10 See also
- 11 References
- 12 External links
Most understanding of the biology of sea lice, other than the early morphological studies, is based on laboratory studies designed to understand issues associated with sea lice infecting fish on salmon farms. Information on sea lice biology and interactions with wild fish is sparse in most areas with a long-term history of open net-cage development, since understanding background levels of sea lice and transfer mechanisms have rarely been a condition of tenure license for farm operators.
Many sea louse species are specific with regard to host genera, for example L. salmonis which has high specificity for salmonids, including the widely farmed Atlantic salmon (Salmo salar). Lepeophtheirus salmonis can parasitize other salmonids to varying degrees, including brown trout (sea trout: Salmo trutta), Arctic char (Salvelinus alpinus), and all species of Pacific salmon. In the case of Pacific salmon, coho, chum, and pink salmon (Oncorhynchus kisutch, O. keta, and O. gorbuscha, respectively) mount strong tissue responses to attaching L. salmonis, which lead to rejection within the first week of infection. Pacific L. salmonis can also develop, but not complete, its full lifecycle on the three-spined stickleback (Gasterosteus aculeatus). This has not been observed with Atlantic L. salmonis.
How planktonic stages of sea lice disperse and find new hosts is still not completely known. Temperature, light, and currents are major factors and survival depends on salinity above 25 ‰. It has been hypothesized that L. salmonis copepodids migrating upwards towards light and salmon smolt moving downwards at daybreak facilitate in finding a host. Several field and modeling studies on L. salmonis have examined copepodid populations and have shown that planktonic stages can be transported tens of kilometres from their source.
The source of L. salmonis infections when salmon return from fresh water has always been a mystery. Sea lice die and fall off anadromous fish such as salmonids when they return to fresh water. Atlantic salmon return and travel upstream in the fall to reproduce, while the smolts do not return to salt water until the next spring. Pacific salmon return to the marine nearshore starting in June, and finish as late as December, dependent upon species and run timing, whereas the smolts typically outmigrate starting in April, and ending in late August, dependent upon species and run timing.
Sea lice possibly survive on fish that remain in the estuaries or they transfer to an as yet unknown alternate host to spend the winter. Smolt get infected with sea lice larvae, or even possibly adults, when they enter the estuaries in the spring. How sea lice distribute between fish in the wild also is not known. Adult stages of Lepeophtheirus spp. can transfer under laboratory conditions, but the frequency is low. Caligus spp. transfer quite readily and between different species of fish, and are regularly found in the plankton.
L. salmonis tends to be about twice the size of most Caligus spp. (e.g. C. elongatus, C. clemensi, etc.). The body consists of four regions: cephalothorax, fourth (leg-bearing) segment, genital complex, and abdomen. The cephalothorax forms a broad shield that includes all of the body segments up to the third leg-bearing segment. It acts like a suction cup in holding the louse on the fish. All species have mouth parts shaped as a siphon or oral cone (characteristic of the Siphonostomatoida). The second antennae and oral appendages are modified to assist in holding the parasite on the fish. The second pair of antennae is also used by males to grasp the female during copulation. The adult females are always significantly larger than males and develop a very large genital complex, which in many species makes up the majority of the body mass. Two egg strings of 500 to 1000 eggs (L. salmonis), which darken with maturation, are roughly the same length as the female’s body. One female can produce 6-11 pairs of egg strings in a lifetime around 7 months.
Sea lice have both free-swimming (planktonic) and parasitic life stages, all separated by moults. The development rate for L. salmonis from egg to adult varies from 17 to 72 days depending on temperature. The lifecycle of L. salmonis is shown in the figure; the sketches of the stages are from Schram.
Eggs hatch into nauplii I, which moult to a second naupliar stage; both naupliar stages are nonfeeding, depending on yolk reserves for energy, and adapted for swimming. The copepodid stage is the infectious stage and it searches for an appropriate host, likely by chemo- and mechanosensory clues. Currents, salinity, light, and other factors also assist copepodids in finding a host. Preferred settlement on the fish occurs in areas with the least hydrodynamic disturbance, particularly the fins and other protected areas. Copepodids once attached to a suitable host feed for a period of time prior to moulting to the chalimus I stage. Sea lice continue their development through three additional chalimus stages each separated by a moult. A characteristic feature of all four chalimus stages is that they are physically attached to the host by a structure referred to as the frontal filament. Differences in the timing, method of production, and the physical structure of the frontal filament are seen between different species of sea lice. With exception of a short period during the moult, the preadult and adult stages are mobile on the fish, and in some cases, can move between host fish. Adult females, being larger, occupy relatively flat body surfaces on the posterior ventral and dorsal midlines and may actually outcompete preadults and males at these sites.
The naupliar and copepodid stages until they locate a host are nonfeeding and live on endogenous food stores. Once attached to the host, the copepodid stage begins feeding and begins to develop into the first chalimus stage. Copepods and chalimus stages have a developed gastrointestinal tract and feed on host mucus and tissues within range of their attachment. Preadult and adult sea lice, especially gravid females, are aggressive feeders, in some cases feeding on blood in addition to tissue and mucus. Blood is often seen in the digestive tract, especially of adult females. L. salmonis is known to secrete large amounts of trypsin into its host’s mucus, which may assist in feeding and digestion. Other compounds such as, prostaglandin E2, have also been identified in L. salmonis secretions and may assist in feeding and/or serve the parasite in avoiding the immune response of the host by regulating it at the feeding site. Whether sea lice are vectors of disease is unknown, but they can be carriers of bacteria and viruses likely obtained from their attachment to and feeding on tissues of contaminated fish.
Sea lice cause physical and enzymatic damage at their sites of attachment and feeding, which results in abrasion-like lesions that vary in their nature and severity depending upon a number of factors, including host species, age, and general health of the fish. Whether stressed fish are particularly prone to infestation is unclear. Sea-lice infection causes a generalized chronic stress response in fish since feeding and attachment cause changes in the mucus consistency and damage the epithelium resulting in loss of blood and fluids, electrolyte changes, and cortisol release. This can decrease salmon immune responses and make them susceptible to other diseases and reduce growth and performance.
The degree of damage is also dependent on the species of sea lice, the developmental stages that are present, and the number of sea lice on a fish. Little evidence exists of host tissue responses in Atlantic salmon at the sites of feeding and attachment, regardless of the development stage. In contrast, coho and pink salmon show strong tissue responses to L. salmonis characterized by epithelial hyperplasia and inflammation. This results in rejection of the parasite within the first week of infection in these species of salmonids. Heavy infections of farmed Atlantic salmon and wild sockeye salmon (Oncorhynchus nerka) by L. salmonis can lead to deep lesions, particularly on the head region, even exposing the skull.
Interactions between wild and farmed fish
Some evidence indicates that sea lice flourishing on salmon farms can spread to nearby wild juvenile salmon and devastate these populations. Sea lice, particularly L. salmonis and various Caligus species, including C. clemensi and C. rogercresseyi, can cause deadly infestations of both farm-grown and wild salmon. Sea lice migrate and latch onto the skin of wild salmon during free-swimming, planktonic nauplii and copepodid larval stages, which can persist for several days. Large numbers of highly populated, open-net salmon farms can create exceptionally large concentrations of sea lice. When exposed in river estuaries containing large numbers of open-net farms, mathematical models have suggested that many young wild salmon may be infected  Adult salmon may survive otherwise critical numbers of sea lice, but small, thin-skinned juvenile salmon migrating to sea are highly vulnerable. Sea trout populations in recent years may have seriously declined due to infestation by sea lice, and Krkosek et al. have claimed that on the Pacific coast of Canada the louse-induced mortality of pink salmon in some regions is over 80%. A few studies indicated no long-term damage to fish stocks in some locations, and a population decline in wild salmon that occurred in 2002 was caused by "something other than sea lice". However, the repeated epizootics of lice on wild fish have only occurred in areas with salmon farms in Ireland, Scotland, Norway, British Columbia, and Chile. Field sampling of copepodids, and hydrographic and population models, show how L. salmonis from farms can cause mass infestations of seaward-migrating salmonids, and this effect can occur up to 30 km (19 mi) from the farms.
Several scientific studies have suggested that caged, farmed salmon harbour lice to a degree that can destroy surrounding wild salmon populations. Other studies have shown that lice from farmed fish have relatively no effect on wild fish if good husbandry and adequate control measures are carried out (see section: Control on salmon farms). Further studies to establish wild–farmed fish interactions are ongoing, particularly in Canada, Scotland, Ireland, and Norway. A reference manual with protocol and guidelines for studying wild/cultured fish interactions with sea lice has been published.
Control on salmon farms
This has been reviewed by Pike & Wadsworth, McVicar, and Costello. Integrated pest management programs for sea lice are instituted or recommended in a number of countries, including Canada, Norway, Scotland, and Ireland. Identification of epidemiological factors as potential risk factors for sea lice abundance with effective sea lice monitoring programs have been shown to effectively reduce sea lice levels on salmon farms.
Cleaner fish, including five species of wrasse (Labridae), are used on fish farms in Norway and to a lesser extent in Scotland, Shetland and Ireland. Their potential has not been researched in other fish farming regions, such as Pacific and Atlantic Canada or Chile.
Good husbandry techniques include fallowing, removal of dead and sick fish, prevention of net fouling, etc. Bay management plans are in place in most fish farming regions to keep sea lice below a level that could lead to health concerns on the farm or affect wild fish in surrounding waters. These include separation of year classes, counting and recording of sea lice on a prescribed basis, use of parasiticides when sea lice counts increase, and monitoring for resistance to parasiticides.
Early findings suggested genetic variation in the susceptibility of Atlantic salmon to Caligus elongatus. Research then began to identify trait markers, and recent studies have shown that susceptibility of Atlantic salmon to L. salmonis can be identified to specific families and that there is a link between MHC Class II and susceptibility to lice.
In October, 2012, The grocery chain Sobeys pulled whole Atlantic salmon from 84 store locations in the Canadian Maritimes after concerns were raised over sea lice. 
In 2017 Salmon prices in Norway increased by 15% over a 3 month period because of a Sea Lice outbreak. 
Drugs and vaccines
The range of therapeutants for farmed fish was limited, often due to regulatory processing limitations. All drugs used have been assessed for environmental impact and risks. The parasiticides are classified into bath and in-feed treatments as follows:
There are both advantages and disadvantages to using bath treatments. Bath treatments are more difficult and need more manpower to administer, requiring skirts or tarpaulins to be placed around the cages to contain the drug. Prevention of reinfection is a challenge since it is practically impossible to treat an entire bay in a short time period. Since the volume of water is imprecise, the required concentration is not guaranteed. Crowding of fish to reduce the volume of drug can also stress the fish. Recent use of well-boats containing the drugs has reduced both the concentration and environmental concerns, although transferring fish to the well boat and back to the cage can be stressful. The major advantage to bath treatments is that all the fish will be treated equally, in contrast to in-feed treatments where amount of drug ingested can vary due to a number of reasons.
Organophosphates are acetylcholinesterase inhibitors and cause excitatory paralysis leading to death of sea lice when given as a bath treatment. Dichlorvos was used for many years in Europe and later replaced by azamethiphos, the active ingredient in Salmosan, which is safer for operators to handle. Azamethiphos is water-soluble and broken down relatively quickly in the environment. Resistance to organophosphates began to develop in Norway in the mid 1990s, apparently due to acetylcholinesterases being altered due to mutation. Use has declined considerably with the introduction of SLICE, emamectin benzoate.
Pyrethroids are direct stimulators of sodium channels in neuronal cells, inducing rapid depolarization and spastic paralysis leading to death. The effect is specific to the parasite since the drugs used are only slowly absorbed by the host and rapidly metabolized once absorbed. Cypermethrin (Excis, Betamax) and deltamethrin (Alphamax) are the two pyrethroids commonly used to control sea lice. Resistance to pyrethroids has been reported in Norway and appears to be due to a mutation leading to a structural change in the sodium channel which prevents pyrethroids from activating the channel. Use of deltamethrin has been increasing as an alternate treatment with the rise in resistance observed with emamectin benzoate.
Bathing fish with hydrogen peroxide (350–500 mg/L for 20 min) will remove mobile sea lice from fish. It is environmentally friendly since H2O2 dissociates to water and oxygen, but can be toxic to fish, depending on water temperature, as well as to operators. It appears to knock the sea lice off the fish, leaving them capable of reattaching to other fish and reinitiating an infection.
In-feed treatments are easier to administer and pose less environmental risk than bath treatments. Feed is usually coated with the drug and drug distribution to the parasite is dependent on the pharmacokinetics of the drug getting in sufficient quantity to the parasite. The drugs have high selective toxicity for the parasite, are quite lipid-soluble so that there is sufficient drug to act for approximately 2 months, and any unmetabolized drug is excreted so slowly that there are little to no environmental concerns.
Avermectins belong to the family of macrocyclic lactones and are the major drugs used as in-feed treatments to kill sea lice. The first avermectin used was ivermectin at doses close to the therapeutic level and was not submitted for legal approval for use on fish by its manufacturer. Ivermectin was toxic to some fish, causing sedation and central nervous system depression due to the drug’s ability to cross the blood–brain barrier. Emamectin benzoate, which is the active agent in the formulation SLICE, has been used since 1999 and has a greater safety margin on fish. It is administered at 50 µg/kg/day for 7 days and is effective for two months, killing both chalimus and mobile stages. Withdrawal times vary with jurisdiction from 68 days in Canada to 175 degree days in Norway. Avermectins act by opening glutamate-gated chloride channels in arthropod neuromuscular tissues, causing hyperpolarization and flaccid paralysis leading to death. Resistance has been noted in Chalimus rogercresseyi in Chile and L. salmonis on North Atlantic fish farms. The resistance is likely due to prolonged use of the drug leading to up-regulation of P-glycoprotein, similar to what has been seen in nematode resistance to macrocyclic lactones.
Teflubenzuron, the active agent in the formulation Calicide, is a chitin synthesis inhibitor and prevents moulting. It thus prevents further development of larval stages of sea lice, but has no effect on adults. It has been used only sparingly in sea lice control, largely due to concerns that it may affect the moult cycle of non-target crustaceans, although this has not been shown at the concentrations recommended.
A number of studies are underway to examine various antigens, particularly from the gastrointestinal tract and reproductive endocrine pathways, as vaccine targets, but no vaccine against sea lice has been reported to date. Two published studies have tested vaccine candidate antigens against salmon lice, which resulted in a reduced infection rate (Grayson et al. 1995; Carpio et al. 2011).
A more recent advance in the delousing strategy is to use pulsed lasers operating at the wavelength of 550 nm to delouse.
Other points of interest
Branchiurans, family Argulidae, order Arguloida are known as fish lice and parasitize fish in freshwater.
- Shane T. Ahyong; James K. Lowry; Miguel Alonso; Roger N. Bamber; Geoffrey A. Boxshall; Peter Castro; Sarah Gerken; Gordan S. Karaman; Joseph W. Goy; Diana S. Jones; Kenneth Meland; D. Christopher Rogers; Jörundur Svavarsson (2011). "Subphylum Crustacea Brünnich, 1772" (PDF). In Z.-Q. Zhang. Animal biodiversity: an outline of higher-level classification and survey of taxonomic richness. Zootaxa. 3148. pp. 165–191.
- T. Chad Walter & Geoff Boxshall (2011). Walter TC, Boxshall G, eds. "Caligidae". World of Copepods database. World Register of Marine Species. Retrieved January 12, 2012.
- S. Bravo (2003). "Sea lice in Chilean salmon farms". Bulletin of the European Association of Fish Pathologists. 23 (4): 197–200.
- R. Yazawa; M. Yasuike; J. Leong; K. R. von Schalburg; G. A. Cooper; M. Beetz-Sargent; A. Robb; W. S. Davidson; S. R. Jones; B. F. Koop (2008). "EST and mitochondrial DNA sequences support a distinct Pacific form of salmon louse, Lepeophtheirus salmonis". Marine Biotechnology. 10 (6): 741–749. doi:10.1007/s10126-008-9112-y. PMID 18574633.
- Geoff Boxshall (2011). Walter TC, Boxshall G, eds. "Caligus O.F. Müller, 1785". World of Copepods database. World Register of Marine Species. Retrieved January 12, 2012.
- T. Chad Walter & Geoff Boxshall (2011). Walter TC, Boxshall G, eds. "Lepeophtheirus von Nordmann, 1832". World of Copepods database. World Register of Marine Species. Retrieved January 12, 2012.
- G. N. Wagner; M. D. Fast; S. C. Johnson (2008). "Physiology and immunology of Lepeophtheirus salmonis infections of salmonids". Trends in Parasitology. 24 (4): 176–183. doi:10.1016/j.pt.2007.12.010. PMID 18329341.
- S. R. M. Jones; G. Prosperi-Porta; E. Kim; P. Callow; N. B. Hargreaves (2006). "The occurrence of Lepeophtheirus salmonis and Caligus clemensi (Copepoda: Caligidae) on threespine stickleback Gasterosteus aculeatus in coastal British Columbia". Journal of Parasitology. 92 (3): 473–480. doi:10.1645/GE-685R1.1. PMID 16883988.
- M. Costelloe; J. Costelloe; G. O'Donohoe; N. J. Coghlan; M. Oonk; Y. van der Heijden (1998). "Planktonic distribution of sea lice larvae Lepeophtheirus salmonis, in Killary Harbour, west coast of Ireland" (PDF). Journal of the Marine Biological Association of the United Kingdom. 78 (3): 853–874. doi:10.1017/S0025315400044830.
- R. L. Genna; W. Mordue; A. W. Pike; A. J. Mordue-Luntz (2005). "Light intensity, salinity, and host velocity influence presettlement intensity and distribution on hosts by copepodids of sea lice, Lepeophtheirus salmonis". Canadian Journal of Fisheries and Aquatic Sciences. 62 (12): 2675–2682. doi:10.1139/f05-163.
- M. J. Costello (2006). "Ecology of sea lice parasitic on farmed and wild fish" (PDF). Trends in Parasitology. 22 (10): 475–483. doi:10.1016/j.pt.2006.08.006. PMID 16920027.
- Kenneth M. Brooks (2005). "The effects of water temperature, salinity, and currents on the survival and distribution of the infective copepodid stage of sea lice (Lepeophtheirus salmonis) originating on Atlantic salmon farms in the Broughton Archipelago of British Columbia, Canada". Reviews in Fisheries Science. 13 (3): 177–204. doi:10.1080/10641260500207109.
- P. A. Heuch; A. Parsons; K. Boxaspen (1995). "Diel vertical migration: a possible host finding mechanism in salmon lice (Lepeophtheirus salmonis) copepodid?". Canadian Journal of Fisheries and Aquatic Sciences. 52 (4): 681–689. doi:10.1139/f95-069.
- M. A. McKibben; D. W. Hay (2004). "Distributions of planktonic sea lice larvae Lepeophtheirus salmonis in the inter-tidal zone in Loch Torrindon, western Scotland in relation to salmon farm production cycles". Aquaculture Research. 35 (8): 742–750. doi:10.1111/j.1365-2109.2004.01096.x., including how their behaviour results in their being moved towards the coastline and mouth of estuaries
- M. J. Costello (2009). "How sea lice from salmon farms may cause wild salmonid declines in Europe and North America and be a threat to fishes elsewhere". Proceedings of the Royal Society B. 276 (1672): 3385–3394. doi:10.1098/rspb.2009.0771. PMC . PMID 19586950.
- S. C. Johnson; L. J. Albright (1991). "The developmental stages of Lepeophtheirus salmonis (Krøyer, 1837) (Copepoda: Caligidae)". Canadian Journal of Zoology. 69 (4): 929–950. doi:10.1139/z91-138.
- M. Anstensrud (1990). "Moulting and mating in Lepeophtheirus pectoralis (Copepoda: Caligidae)". Journal of the Marine Biological Association of the United Kingdom. 70 (2): 269–281. doi:10.1017/S0025315400035396.
- A. Mustafa; G. A. Conboy; J. F. Burka (2001). "Life-span and reproductive capacity of sea lice, Lepeophtheirus salmonis, under laboratory conditions". Aquaculture Association of Canada Special Publication. 4: 113–114.
- Thomas A. Schram (1993). "Supplementary description of the developmental stages of Lepeophtheirus salmonis (Krøyer, 1837) (Copepoda: Caligidae)". In G. A. Boxshall; D. Defaye. Pathogens of Wild and Farmed Fish: Sea Lice. Chichester: Ellis Horwood. pp. 30–50. ISBN 0-13-015504-7.
- A. W. Pike; S. L. Wadsworth (1999). "Sealice on salmonids: their biology and control". Advances in Parasitology. 44: 233–337. doi:10.1016/S0065-308X(08)60233-X. ISBN 978-0-12-031744-8. PMID 10563397.
- J. E. Bron; C. Sommerville; M. Jones; G. H. Rae (1991). "The settlement and attachment of early stages of the salmon louse, Lepeophtheirus salmonis (Copepoda: Caligidae) on the salmon host Salmo salar". Journal of Zoology. 224 (2): 201–212. doi:10.1111/j.1469-7998.1991.tb04799.x.
- C. D. Todd; A. M. Walker; J. E. Hoyle; S. J. Northcott; A. F. Walker; M. G. Ritchie (2000). "Infestations of wild adult Atlantic salmon (Salmo salar L.) by the ectoparasitic copepod sea louse Lepeophtheirus salmonis (Krøyer): prevalence, intensity and the spatial distribution of males and females on the host fish". Hydrobiologia. 429 (2–3): 181–196. doi:10.1023/A:1004031318505.
- Kara J. Firth; Stewart C. Johnson; Neil W. Ross (2000). "Characterization of proteases in the skin mucus of Atlantic salmon (Salmo salar) infected with the salmon louse (Lepeophtheirus salmonis) and in whole-body louse homogenates". Journal of Parasitology. 86 (6): 1199–1205. doi:10.1645/0022-3395(2000)086[1199:COPITS]2.0.CO;2. JSTOR 3285000. PMID 11191891.
- M. D. Fast; N. W. Ross; S. C. Johnson (2005). "Prostaglandin E2 modulation of gene expression in an Atlantic salmon (Salmo salar) macrophage-like cell line (SHK-1)". Developmental & Comparative Immunology. 29 (11): 951–963. doi:10.1016/j.dci.2005.03.007. PMID 15936074.
- A. Nylund; B. Bjørknes; C. Wallace (1991). "Lepeophtheirus salmonis – a possible vector in the spread of diseases on salmonids". Bulletin of the European Association of Fish Pathologists. 11 (6): 213–216.
- S. C. Johnson; L. J. Albright (1992). "Effects of cortisol implants on the susceptibility and the histopathology of the responses of naive coho salmon Oncorhynchus kisutch to experimental infection with Lepeophtheirus salmonis (Copepoda : Caligidae)". Diseases of Aquatic Organisms. 14: 195–205. doi:10.3354/dao014195.
- N. W. Ross; K. J. Firth; A. Wang; J. F. Burka; S. C. Johnson (2000). "Changes in hydrolytic enzyme activities of naive Atlantic salmon (Salmo salar) skin mucus due to infection with the salmon louse (Lepeophtheirus salmonis) and cortisol implantation". Diseases of Aquatic Organisms. 41 (1): 43–51. doi:10.3354/dao041043. PMID 10907138.
- M. Krkosek; J. S. Ford; A. Morton; S. Lele; R. A. Myers; M. A. Lewis (2007). "Declining wild salmon populations in relation to parasites from farm salmon". Science. 318 (5857): 1772–5. doi:10.1126/science.1148744. PMID 18079401.
- "Sea lice and salmon: elevating the dialogue on the farmed–wild salmon story" (PDF). Watershed Watch Salmon Society. 2004. Archived from the original (PDF) on December 14, 2010. Retrieved January 15, 2010.
- A. Morton; R. Routledge; C. Peet; A. Ladwig (2004). "Sea lice (Lepeophtheirus salmonis) infection rates on juvenile pink (Oncorhynchus gorbuscha) and chum (Oncorhynchus keta) salmon in the nearshore marine environment of British Columbia, Canada". Canadian Journal of Fisheries and Aquatic Sciences. 61 (2): 147–157. doi:10.1139/f04-016.
- Corey Ryan Peet (2007). Interactions between sea lice (Lepeoptheirus salmonis and Caligus clemensii), juvenile salmon (Oncorhynchus keta and Oncorhynchus gorbuscha) and salmon farms in British Columbia (M.Sc. thesis). University of Victoria.
- M. Krkošek; A. Gottesfeld; B. Proctor; D. Rolston; C. Carr-Harris; M. A. Lewis (2007). "Effects of host migration, diversity and aquaculture on sea lice threats to Pacific salmon populations". Proceedings of the Royal Society B. 274 (1629): 3141–3149. doi:10.1098/rspb.2007.1122. PMC . PMID 17939989.
- A. Morton; R. Routledge; M. Krkošek (2008). "Sea louse infestation in wild juvenile salmon and Pacific herring associated with fish farms off the east-central coast of Vancouver Island, British Columbia" (PDF). North American Journal of Fisheries Management. 28 (2): 523–532. doi:10.1577/M07-042.1.[permanent dead link]
- M. Krkošek; M. A. Lewis; A. Morton; L. N. Frazer; J. P. Volpe (2006). "Epizootics of wild fish induced by farm fish". Proceedings of the National Academy of Sciences. 103 (42): 15506–15510. doi:10.1073/pnas.0603525103. PMC . PMID 17021017.
- Charles Clover (2004). The End of the Line: How Overfishing is Changing the World and What We Eat. London: Ebury Press. ISBN 0-09-189780-7.
- S. R. M. Jones; N. B. Hargreaves (2009). "Infection threshold to estimate Lepeophtheirus salmonis-associated mortality among juvenile pink salmon" (PDF). Diseases of Aquatic Organisms. 84: 131–137. doi:10.3354/dao02043. PMID 19476283.
- Gary D. Marty; S. M. Saksida; T. J. Quinn II (2010). "Relationship of farm salmon, sea lice, and wild salmon populations". Proceedings of the National Academy of Sciences. 107 (52): 22599–22604. doi:10.1073/pnas.1009573108. PMC . PMID 21149706.
- M. J. Costello (2009). "The global economic cost of sea lice to the salmonid farming industry". Journal of Fish Diseases. 32: 115–118. doi:10.1111/j.1365-2761.2008.01011.x.
- Peter Andreas Heuch; Pål Arne Bjørn; Bengt Finstad; Jens Christian Holst; Lars Asplin; Frank Nilsen (2005). "A review of the Norwegian 'National Action Plan Against Salmon Lice on Salmonids': The effect on wild salmonids". Aquaculture. 246 (1–4): 79–92. doi:10.1016/j.aquaculture.2004.12.027.
- "Protocols and Guidelines: A Reference Manual for Research Involving Wild/Cultured Fish Interactions with Sea Lice". Pacific Salmon Forum. Retrieved September 17, 2009.
- Alasdair H. McVicar (2004). "Management actions in relation to the controversy about salmon lice infections in fish farms as a hazard to wild salmonid populations". Aquaculture and Research. 35 (8): 751–758. doi:10.1111/j.1365-2109.2004.01097.x.
- Integrated Pest Management of Sea Lice in Salmon Aquaculture. Health Canada. ISBN 0-662-34002-7. Retrieved March 26, 2010.
- "Sea Lice Management Strategy 2007/2008" (PDF). British Columbia Ministry of Agriculture and Lands. Retrieved September 11, 2009.
- A. J. Rosie; P. T. R. Singleton (2002). "Discharge consents in Scotland". Pest Management Science. 58 (6): 616–621. doi:10.1002/ps.475.
- B. Grist (2002). "The regulatory system for aquaculture in the Republic of Ireland". Pest Management Science. 58 (6): 609–615. doi:10.1002/ps.512. PMID 12138627.
- C. W. Revie; G. Getinby; J. W. Treasurer; C. Wallace (2003). "Identifying epidemiological factors affecting sea lice Lepeophtheirus salmonis abundance on Scottish salmon farms using general linear models". Diseases of Aquatic Organisms. 57 (1–2): 85–95. doi:10.3354/dao057085. PMID 14735925.
- S. Saksida; G. A. Karreman; J. Constantine; A. Donald (2007). "Differences in Lepeophtheirus salmonis abundance levels on Atlantic salmon farms in the Broughton Archipelago, British Columbia, Canada". Journal of Fish Diseases. 30 (6): 357–366. doi:10.1111/j.1365-2761.2007.00814.x. PMID 17498179.
- James W. Treasurer (2002). "A review of potential pathogens of sea lice and the application of cleaner fish in biological control". Pest Management Science. 58 (6): 546–558. doi:10.1002/ps.509. PMID 12138621.
- A. Mustafa; B. M. MacKinnon (1999). "Genetic variation in susceptibility of Atlantic salmon to the sea louse Caligus elongatus Nordmann 1882". Canadian Journal of Zoology. 77 (8): 1332–1335. doi:10.1139/cjz-77-8-1332.
- Catherine S. Jones; Anne E. Lockyer; Eric Verspoor; Christopher J. Secombes; Leslie R. Noble (2002). "Towards selective breeding of Atlantic salmon for sea louse resistance: approaches to identify trait markers". Pest Management Science. 58 (6): 559–568. doi:10.1002/ps.511. PMID 12138622.
- K. A. Glover; U. Grimholt; H. G. Bakke; F. Nilsen; A. Storset; Ø. Skaala (2007). "Major histocompatibility complex (MHC) variation and susceptibility to the sea louse Lepeophtheirus salmonis in Atlantic salmon Salmo salar". Diseases of Aquatic Organisms. 76 (1): 57–66. doi:10.3354/dao076057. PMID 17718166.
- L. E. Burridge (2003). "Chemical use in marine finfish aquaculture in Canada: A review of current practices and possible environmental effects". Canadian Technical Reports of Fisheries and Aquatic Sciences. 2450: 97–131.
- K. Haya; L. E. Burridge; I. M. Davies; E. Ervik (2005). "A review and assessment of environmental risk of chemicals used for the treatment of sea lice infestations of cultured salmon". The Handbook of Environmental Chemistry. Handbook of Environmental Chemistry. 5 (M): 305–340. doi:10.1007/b136016. ISBN 3-540-25269-X.
- I. Denholm; G. J. Devine; T. E. Horsberg; S. Sevatdal; A. Fallang; D. V. Nolan; R. Powell (2002). "Analysis and management of resistance to chemotherapeutants in salmon lice Lepeophtheirus salmonis (Copepoda: Caligidae)". Pest Management Science. 58 (6): 528–536. doi:10.1002/ps.482. PMID 12138619.
- Anders Fallang; Jennifer Mara Ramsay; Sigmund Sevatdal; John F. Burka; Philip Jewess; K. Larry Hammell; Tor E. Horsberg (2004). "Evidence for occurrence of an organophosphate-resistant type of acetylcholinesterase in strains of sea lice (Lepeophtheirus salmonis Krøyer)". Pest Management Science. 60 (12): 1163–1170. doi:10.1002/ps.932. PMID 15578596.
- A. Fallang; I. Denholm; T. E. Horsberg; M. S. Williamson (2005). "Novel point mutation in the sodium channel gene of pyrethroid-resistant sea lice Lepeophtheirus salmonis (Crustacea: Copepoda)". Diseases of Aquatic Organisms. 65 (2): 129–136. doi:10.3354/dao065129. PMID 16060266.
- A. N. Grant (2002). "Medicines for sea lice". Pest Management Science. 58 (6): 521–527. doi:10.1002/ps.481. PMID 12138618.
- "Slice* Premix". Schering-Plough Animal Health. Retrieved September 11, 2009.
- "Depletion of Emamectin Benzoate (SLICE®) from Skeletal Muscle (and Skin) of Atlantic Salmon (Salmo salar) following a Multiple Oral (Dietary) 50 µg/kg Dose Regimen, in Seawater at 10 ±1°C; One Laboratory and Two Field-based trials". MG-06-04-004. Fisheries and Oceans Canada. 31 March 2007. Retrieved 4 March 2011.
- N. D. Tribble; J. F. Burka; F. S. B. Kibenge; G. M. Wright (2008). "Identification and localization of a putative ATP-binding cassette transporter in sea lice (Lepeophtheirus salmonis) and host Atlantic salmon (Salmo salar)". Parasitology. 135 (2): 243–255. doi:10.1017/S0031182007003861. PMID 17961285.
- Anne Lespine; Michel Alvinerie; Jozef Vercruysse; Roger K. Prichard; Peter Geldhof (2008). "ABC transporter modulation: a strategy to enhance the activity of macrocyclic lactone anthelmintics". Trends in Parasitology. 24 (7): 293–298. doi:10.1016/j.pt.2008.03.011. PMID 18514030.
- EMEA (1999). "Teflubenzuron, summary report" (PDF). Retrieved September 11, 2009.
- Grayson, T. H.; John, R. J.; Wadsworth, S.; Greaves, K.; Cox, D.; Roper, J.; Wrathmell, A. B.; Gilpin, M. L.; Harris, J. E. (1995-12-01). "Immunization of Atlantic salmon against the salmon louse: identification of antigens and effects on louse fecundity". Journal of Fish Biology. 47: 85–94. doi:10.1111/j.1095-8649.1995.tb06046.x. ISSN 1095-8649.
- Carpio, Yamila; Basabe, Liliana; Acosta, Jannel; Rodríguez, Alina; Mendoza, Adriana; Lisperger, Angélica; Zamorano, Eugenio; González, Margarita; Rivas, Mario. "Novel gene isolated from Caligus rogercresseyi: A promising target for vaccine development against sea lice". Vaccine. 29 (15): 2810–2820. doi:10.1016/j.vaccine.2011.01.109. PMID 21320542.
- "Lice-Hunting Underwater Drone Protects Salmon With Lasers". IEEE Spectrum: Technology, Engineering, and Science News. Retrieved 2017-06-05.
|Wikimedia Commons has media related to Caligidae.|
|Wikispecies has information related to Caligidae|
- DFO Canada information on sea-lice 
- Pacific Salmon Forum Interim Results 
- Watershed Watch Salmon Society British Columbia advocacy group for wild salmon.
- Wild Salmon in Trouble: The Link Between Farmed Salmon, Sea Lice and Wild Salmon - Watershed Watch Salmon Society. Animated short film based on peer-reviewed scientific research.
- Aquacultural Revolution: The scientific case for changing salmon farming - Watershed Watch Salmon Society. Short video documentary by filmmakers Damien Gillis and Stan Proboszcz. Prominent scientists and First Nation representatives speak their minds about the salmon farming industry and the effect of sea lice infestations on wild salmon populations.
- Sea Lice - Coastal Alliance for Aquaculture Reform. Overview of farmed to wild salmon interactive effects of sea lice.
- Salmon Farming Problems - Coastal Alliance for Aquaculture Reform. Overview of environmental impacts of salmon farming.
- Fish farms drive wild salmon populations toward extinction Biology News Net. December 13, 2007.
- Ecological Genetics of Parasitic Sea Lice University of St Andrews Marine Ecology Research Group.
- Sea Lice expert reviewed and published by WikiVet