|New Zealand green-lipped mussel|
|Close-up of the green lip of this mussel species|
The New Zealand green-lipped mussel, (Perna canaliculus), also known as the New Zealand mussel, the greenshell mussel, kuku, and kutai, is a bivalve mollusc in the family Mytilidae the true mussels. P. canaliculus has great importance as a cultivated species in New Zealand.
Perna canaliculus occurs around all of New Zealand's mainland. It is usually found below the intertidal zone, but it can occur in the intertidal zone. P. canaliculus feeds on various types of phytoplankton.
This shellfish is economically important to New Zealand. It differs from other mussel species in that it has dark brown/green shells with green lips around the edges, and only has one adductor muscle. It is also one of the largest mussel species, reaching 240 mm in length.
Studies have found that Perna canaliculus inhibits the 5-lipoxygenase pathway, which leads to the formation of leukotrienes. Many of the products of these pathways have inflammation-supporting properties. However, a systematic review of current scientific research on supplementation with green-lipped mussel suggests a lack of compelling evidence for its use in humans with inflammation associated arthritis.
The New Zealand green-lipped mussel, Perna canaliculus, is endemic to New Zealand. When grown for aquaculture in New Zealand it is produced under the trademark name Greenshell. The New Zealand greenshell mussel aquaculture industry produces over 140,000 tonnes annually and in 2009 was valued in excess of NZ$250 million. The aquaculture of the New Zealand greenshell mussel relies heavily on the production of mussel seed, or spat, by wild mussel populations. Around 270 tonnes of wild spat which is attached to beach-cast seaweed is collected from Ninety Mile Beach in northern New Zealand each year to supply the aquaculture industry. Nowhere else in the country are there such large quantities of mussel covered seaweed washed ashore. The density of spat varies from 200 to 2 million per kilogram of seaweed. This single beach provides around 80% of the seed mussels required for this aquaculture industry. The remaining 20% is caught using fibrous ropes which are suspended in the sea near mussel farms. Even with this industry’s heavy dependency on wild spat, the biological and environmental processes by which the spat arrives on Ninety Mile Beach and on spat collection ropes are largely unknown. Furthermore, the amount of mussel spat that lands on Ninety Mile Beach is highly variable. This uncertainty of supply has resulted in major production problems for the industry which must endure periods of up to a year without the arrival of any spat. ‘Spatfall’ events are also affected by El Nino periods and can result in delays in mussel farm production due to the insufficient seed landing on Ninety Mile Beach.
New Zealand greenshell mussel cultivation began in the 1970s and has since undergone massive expansion, with production growth of 708% from 1988 to 2000 (an average annual growth of 18%). Initial farms were based on the 700-year-old European floating raft method of mussel cultivation which was suitable at small scales, however, it was not long before methods to support larger scale production were needed. An adaption of the Japanese longline shellfish aquaculture system led to the methods used today for commercial greenshell aquaculture and facilitated the transition to large scale production by incorporating mechanized harvesting. This adaptation of the Japanese longline method consists of a series of large plastic buoys connected by two ropes forming a backbone which is held in place by concrete anchor blocks or steel anchors screwed into the seabed. Once the spat have been transported from the beach to mussel farms around the country they are transferred into a stocking that holds the spat covered seaweed material around a “dropper rope” which is suspended in the water column hanging at regular intervals off the backbone ropes. Soon afterwards the stocking and seaweed rots away leaving only the rope for the mussels to attach. Subsequent loss of spat from the dropper ropes is typically high, generally over 50% and as high as 95%. This loss is partly due to the secondary settlement behaviour of mussels, whereby the spat can release their point of attachment to the growing rope and exude a mucous “parachute” to help move to an alternative settlement site using water currents. This loss of spat from mussel farms is a significant problem for the industry and research into what exactly causes the mussels to detach from the rope is needed. A 2007 study identified two stressors that reduce the retention of mussels on the rope; desiccation and starvation (both of which are experienced on the journey from where the spat are harvested to where they are farmed). Steps to reduce these stressors on the spat during transport could potentially improve retention rates.
Growing mussels are removed from the dropper ropes and re-seeded once and sometimes twice before reaching harvesting size of around 100 mm. Harvesting is achieved using specially designed vessels which allow the dropper ropes to be pulled on board to strip the mussels from the dropper rope. From the initial seeding of mussels onto farms until harvesting takes from 12 to 24 months. The productivity of mussel farms is around 9.85 tonnes per hectare each year, which is 200 times the productivity of protein from land-based farming.
Mussel farming is a fast-growing industry in New Zealand. In the year 2000 there were 3000 hectares of mussel farms and proposals for another 30,000 ha. Typically individual farms are less than 50 ha and placed in sheltered waters close to the shore. With more recent technological developments larger mussel farms can now be constructed further offshore and in more exposed waters.
After 15 years of research and development into hatchery production of spat the industry still remains almost completely reliant on wild spat. This is because collecting wild spat is markedly cheaper than breeding mussels in a hatchery. However, it is likely hatcheries will become increasingly important in greenshell mussel aquaculture for two main reasons. First, the potential for producing a more valuable product because hatcheries are able to selectively breed for desired traits. Second, the reliability of hatchery seed is a more stable base for an industry relying on wild seed, particularly in years when wild spat numbers are low, and when the hatchery spat will attract a premium.
The New Zealand greenshell mussel industry operates within some of the strictest quality standards in the world  Both the mussels and seawater around the farms are tested for biotoxins, bacteria, and heavy metals. The water quality is constantly monitored with tests carried out to the standards set by the U.S Food and Drug Administration, European Union, and NZ Food Safety Authority. The standards are in place to meet the increasing global demand for safe and healthy seafood products. The Resource Management Act 1991 and Fisheries Act 1996 have been put in place by the New Zealand government to mitigate the environmental effects of aquaculture in New Zealand. New Zealand’s high aquaculture standards have been recognized by the International Conservation Organisation Blue Ocean Institute, which ranked New Zealand greenshell mussels as one of the top two ‘eco-friendly seafoods’ in the world.
New Zealand greenshell mussel are often parasitized by pea crabs. In 2015, New Zealand researchers Oliver Trottier and Andrew Jeffs from University of Auckland studied  the mate location behaviour of male New Zealand pea crabs, which were observed when dwelling in the mussel. Given the cryptic behaviour of the male crabs, a trapping system was developed to determine whether male crabs would exit their mussel hosts in response to an upstream female crab. Observations of the nocturnal mate-finding behaviour of male crabs were made in darkness using infrared video recordings. Male crabs were often observed stroking the mantle edge of the mussel whilst attempting to gain entry, successfully increasing mussel valve gape during entry from 3.7 to 5.5 mm.
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