Paranephrops Northern koura, P. planifrons Scientific classification Kingdom: Animalia Phylum: Arthropoda Subphylum: Crustacea Class: Malacostraca Order: Decapoda Infraorder: Astacidea Family: Parastacidae Genus: Paranephrops
- P. planifrons White, 1842
- P. zealandicus (White, 1847)
Paranephrops is a genus of freshwater crayfish species endemic to New Zealand. They are known as koura in New Zealand, derived from the Māori language. The two species are divided by the Southern Alps of New Zealand's South Island.
The Northern koura, Paranephrops planifrons, is found mainly in the North Island, but also in Marlborough, Nelson and the West Coast of the South Island. They reach lengths of about 70 millimetres (2.8 in).
The Southern koura, Paranephrops zealandicus, is found only in the east and south of the South Island, and on Stewart Island/Rakiura. They reach lengths of about 80 millimetres (3.1 in). Koura occupy freshwater streams, lakes, rivers and swamps. Koura use their 4 pairs of walking legs to move through their environment and when alarmed can flick their tail forwards violently to propel themselves backwards at speed in order to avoid any threat. The koura's first pair of legs (chelae) are pincers that are used for scavenging, food and warding off predators or other koura.
Koura like all crustaceans moult their exoskeletons in order to increase in size. During moulting the carapace becomes soft with calcium being resorbed and the remaining outer shell shed. The new carapace forms underneath where it takes a number of days to harden. Calcium for this new outer shell comes from gastroliths that line the stomach wall of the koura and these produce around 10%–20% of the calcium needs for exoskeleton production. The gastroliths drop into the koura's foregut where they are broken down to allow the adsorption of calcium. Post moulting the demand for calcium in order to harden the exoskeleton is high and this demand is met in part by the koura eating its discarded exoskeleton. The remaining calcium required to completely harden the exoskeleton is achieved by absorption from the water. Lower limits of 5 mg/L of calcium (Ca) in water for temperate species of koura have been suggested as sufficient to support exoskeleton hardening.
Water temperature and calcium concentrations are thought to be the key variables determining koura growth rates. P. zealandicus have high survivability (>80%) rates below 16 °C (61 °F) but temperatures above this correlate with lower rates of survivability. Higher death rates are thought to be associated with increased activity of koura at higher temperatures. Greater activity by koura increases cannibalistic behaviour and increased activity may also impact on water quality with the greater production of ammonia as a waste product. Survival of koura also increases with higher calcium concentrations in the water and this is thought to be in part due to a lower incidence of moulting related deaths and decreased risk from predation. A calcium concentration value of 20–30 mg/L Ca in water is thought to be ideal for maintaining koura growth and survivability in aquaculture setups.
Koura in natural populations consume a variety of foods with animal protein contributing the most to growth. Invertebrates including aquatic snails, chironomids, and mayflies are the predominant food sources in the koura diet. Juvenile koura require higher amounts of protein in their diet than adults due to greater growth rate demands with invertebrates forming the bulk of their diet. Koura in lakes have been shown to feed predominantly in the littoral zone where food availability is greatest. Feeding in the littoral zone may reflect diel movement with koura moving to deeper and darker parts of lakes to avoid predation during daylight hours and moving to the littoral zone at night in order to feed.
In lakes the type of habitat that koura occupy is largely influenced by light levels, with koura moving into shallower areas of the water column during periods of darkness and deeper parts of the water column during daylight hours. During daytime koura find shelter under rocks, debris such as cans and bottles, and vegetation. In soft sediments koura may also excavate fan shaped depressions with this commonly occurring at depths of 12–30 metres (39–98 ft) in some lakes. In streams koura take cover on the bottom beneath fallen leaf litter, fallen logs, and tree roots and undercut banks. Tree fern roots that project into the stream are thought to provide excellent cover for juvenile koura.
Predators, cannibalism and disease
Eels, perch, catfish and trout are the major aquatic predators of koura. Other terrestrial predators include rats, kingfishers, shags, scaup, stoats and kiwi. Shag populations from the Te Arawa lakes district in the North Island of New Zealand have been shown to feed on koura as the bulk of their diet. Predation on koura by trout is thought to be restricted to larger adult trout. Streams and lakes with established populations of trout have been shown to affect koura abundance. Cannibalism in koura is most likely to occur when koura are sick or moulting. Cannibalism can be a greater problem in high density situations where competition for shelter and territory is greatest. Juvenile koura can be consumed whole by larger koura and this presents problems for aquaculture in ensuring continuity of intergenerational growth. Koura use their chelae for both attack and defence and when one limb is lost the koura will divert energy for overall growth to restoring the lost limb. The only disease known to seriously affect koura is "white tail disease" and this is caused by the microsporidian parasite Thelohania contejeani. This parasite causes degeneration of striated muscle in the tail area and this turns the tail a pale white colour and correspondingly leads to death soon after.
The female carries between 20–200 eggs under the side flaps of her abdomen whereby they take 3–4 months to hatch. Over this time male sperm production corresponds with females' reproductivity. Once hatched juvenile koura cling to their mother’s abdomen using their pincers to attach until they have reached a length of 4–10 millimetres (0.16–0.39 in). At this stage they resemble adult koura in appearance. In Lake Rotoiti in the central North Island of New Zealand the main breeding period occurs between April–July (autumn–winter) with a second breeding period occurring from October–January (spring–summer). The total breeding length time from peak egg laying to the release of juveniles is estimated to be 28 weeks for the autumn–winter period and 19–20 weeks in spring–summer breeding groups. This difference is attributed to warmer temperatures speeding up the egg development process. In stream populations this growth period has been shown to take around 25–26 weeks in P. planifrons, and up to 60 weeks for P. zealandicus in Otago streams.
Farming of koura is currently undertaken by a small number of companies within New Zealand. Sweet Koura Enterprises Ltd and New Zealand Clearwater Crayfish Ltd are two such operators. Koura is sold solely to the high end restaurant trade where they are commonly eaten as an entrée dish. Koura are harvestable once larger than 100 mm (3.9 in) in total length which can take between 2-5 years in P. planifrons. Sweet Koura Enterprises Ltd located in Central Otago, within the South Island of New Zealand, farm P. zealandicus in artificial ponds of approximately 200 square metres (2,200 sq ft) in size. These ponds attempt to replicate the natural environment that P. zealandicus grow in. Water supplied to the growing ponds is sourced from an aquifer and is artificially aerated. The temperature of the water is controlled to reflect the seasonal temperature variations that would be expected in the natural environment. The optimum temperature for growth in these ponds is achieved at between 15–18 °C (59–64 °F) with P. zealandicus sensitive to rapid temperature changes. The natural biological life in a pond can support 3–4 koura per square metre. Additional feed in the form of fish based pallets are supplied to koura to support growth and this feed has been altered to reflect the lower protein, higher calcium nutritional requirements of koura. Overstocking of crayfish can lead to higher rates of mortality which is associated with higher rates of cannibalism and increased competition for shelter and food.
New Zealand Clearwater Crayfish Ltd farm the northern koura species P. planifrons using a gravity fed system with pond culture and raceways for farming koura. A key step in this koura farm is the depuration of koura in clean running water without food for up to 2 days in order to purge the gut cavity. This enables the tail to be presented as an appealing white flesh to the consumer.
In order to breed koura in aquaculture a ratio of 1 male to 5 females is suggested during the mating periods with koura removed and placed in separate tanks depending of the life stage once hatched. The creation of artificial habitat in ponds may support koura survival. The use of plastic containers, tyres, plastic piping and bottles are all possible habits for koura to occupy when being grown in ponds. The suggested depth for ponds used to farm P. zealandicus are 1.3–5.0 m (4 ft 3 in–16 ft 5 in) deep.
A number of environmental challenges exist to koura farmers in ensuring optimum growth and survivability of stock. Environmental contamination of freshwater supplied to ponds from other land use activities such as livestock farming can affect Koura survivability. Other risks come from the introduction into the ponds of predators such as carp, eels and birds however these can be controlled by steps such as netting across pond surfaces. Algal blooms creating anoxic conditions and cannibalism caused by high density stocking of ponds is also a challenge to koura farmers.
The outlook for the growth of koura aquaculture in the New Zealand domestic setting may exist with the potential for increasing demand in the restaurant and tourism fields. Export of koura to the international market may offer less potential due to competition from other established freshwater crayfish species such as the red swamp crayfish Procambarus clarkii of which the United States and China annually consume 34,000 tonnes and 88,000 tonnes respectively.
- ^ Kent S. Hammond, John W. Hollows, Colin R. Townsend & P. Mark Lokman (2006). "Effects of temperature and water calcium concentration on growth, survival and moulting of freshwater crayfish, Paranephrops zealandicus". Aquaculture 251 (2–4): 271–279. doi:10.1016/j.aquaculture.2005.05.032.
- ^ a b c d I. Kusabs & S. M. Parkyn (2007). Taonga and Mahinga Kai Species of the Te Arawa Lakes: a Review of Current Knowledge – Koura. National Institute of Water and Atmospheric Research. NIWA Client Report HAM2007-022.
- ^ C. L. Hopkins (1967). "Breeding in the freshwater crayfish Paranephrops planifrons". New Zealand Journal of Marine and Freshwater Research 1: 51–58.
- ^ N. Whitmore (1997 – unpublished). Population ecology of the freshwater crayfish ''Paranephrops zealandicus and its effect on the community structure of a lowland bush stream (M.Sc. thesis). University of Otago.
- ^ a b c d e S. M. Parkyn (1999). A Review of the Biology and Aquaculture Potential of Koura. Hamilton, New Zealand: National Institute of Water and Atmospheric Research.
- ^ a b Customary and Commercial Opportunities for Freshwater Aquaculture. Consultants report. Synexe Consulting Ltd and Nesus and Associates Ltd.. 2009.
- "New Zealand crayfish and shrimps". CrayfishWorld. http://www.crayfishworld.com/nz.htm.
- R. A. Fordham, S. D. Kelton, H. Leersnyder & P. L. Lo (1979). "Subalpine koura, Paranephrops planifrons (Decapoda), in Tongariro National Park: zoogeographic implications". New Zealand Journal of Marine and Freshwater Research 13: 443–446. http://www.royalsociety.org.nz/publications/journals/nzjm/1979/047/.
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