Commercial land-based farming of European lobster (Homarus gammarus L.) in recirculating aquaculture system (RAS) using a single cage approach

Commercial land-based farming of European lobster (Homarus gammarus L.) in recirculating aquaculture system (RAS) using a single cage approach

Accepted Manuscript Title: Commercial land-based farming of European lobster (Homarus gammarus L.) in Recirculating Aquaculture System (RAS) using a s...

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Accepted Manuscript Title: Commercial land-based farming of European lobster (Homarus gammarus L.) in Recirculating Aquaculture System (RAS) using a single cage approach Authors: Asbjørn Drengstig, Asbjørn Bergheim PII: DOI: Reference:

S0144-8609(12)00091-X doi:10.1016/j.aquaeng.2012.11.007 AQUE 1667

To appear in:

Aquacultural Engineering

Received date: Accepted date:

28-9-2012 19-11-2012

Please cite this article as: Drengstig, A., Bergheim, A., Commercial land-based farming of European lobster (Homarus gammarus L.) in Recirculating Aquaculture System (RAS) using a single cage approach, Aquacultural Engineering (2010), doi:10.1016/j.aquaeng.2012.11.007 This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.

Highlights (for review)

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1. Successful production of plate-sized European lobster 2. Respiration and excretion rates of European lobster 3. Water quality in RAS producing European lobster

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*Manuscript

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Commercial land-based farming of European lobster (Homarus gammarus L.) in Recirculating Aquaculture System (RAS) using a single cage approach

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ABSTRACT In the past, farming of the European lobster in land-based systems has turned out to be

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difficult. The ideal system for rearing lobsters individually should be relatively

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inexpensive to construct and operate, simple to maintain, based on automatic feeding

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and self-cleaning of tank and cages, maintain ideal water quality conditions, use space

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in three dimensions, enable high densities, conserve water at high temperatures, ensure

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good survival and permit easy access to the livestock for inspection and feeding.

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Several attempts have been made to mass-produce these cannibalistic crustaceans under

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controlled environments. However, none of the many previous attempts have proved to

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be successful in incorporating all of these features into a single design. Thus, the

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development of land-based lobster farming has been severely hampered by lack of

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suitable technology and production methods. The major constraints have been the need

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for individual rearing cages to avoid cannibalism, need of heated water, lack of high

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quality dry food, high labour costs, inadequate technological solutions and high

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investment costs.

Asbjørn Drengstig1*, Asbjørn Bergheim2 1

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Norwegian Lobster Farm AS, Stavanger, Norway Phone: +47 90196731; Fax: +47 51325901; [email protected] 2 IRIS – International Research Institute of Stavanger, Stavanger, Norway *Corresponding author

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Today, Norwegian Lobster Farm operates the world’s first land-based RAS farm

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producing plate sized lobsters. The company also operates its own brood-stock

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department and a hatchery for production of IV-stage juveniles. The system contains a

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patented single cage technology with moving bed biofilters where the recirculation

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system is designed to fit the water management. Automated solutions for accurate

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feeding, robots supporting mass-rearing of the IV-stage juveniles and image processing

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programs for daily monitoring of each single individual have been developed and

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successfully tested.

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1.

Introduction

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Today, European lobster (Homarus gammarus L.) is considered to be the most

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exclusive seafood product in the world. At present there is a scarce supply of wild

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caught lobster into the international markets, with quantities varying between 2,000 –

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2,500 metric tons (MT) per annum (Agnalt, 2008). In Norway the annual landings have

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declined from 1,000 – 1,300 MT in the early 20th century to 30 – 50 MT from 1980s and

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onwards. This has led to elevated market prices due to an increasing gap between

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supply and demand. Hence, European lobster is a promising candidate for closed-cycle

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aquaculture.

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The attention on full grow-out culture peaked in the 1970’s, when government

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funded research programs on intensive culture of American lobster were conducted in

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USA and Canada (e.g. Coffelt and Wikman-Coffelt, 1985). As a result of this research

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and earlier studies, lobster biology is reasonably well understood (Factor, 1995), seed

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stock can be produced on demand, and systems and strategies are in place for rearing

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lobster from larvae to market size (van Olst et al., 1980; Aiken and Waddy, 1995;

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Nicosia and Lavalli, 1999). Several private companies in America started lobster

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production, but none of these projects proved to be commercially viable (Nicosia and

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Lavalli, 1999). A large increase in landings of wild lobsters and an abrupt termination of

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governmental research programs, before rearing technology and formulated lobster

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feeds were sufficiently developed, contributed to this scenario (Aiken and Waddy,

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1995). Besides, the necessary computer and automation technology was too poorly

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developed by 1995 to achieve a sufficient automation level at a reasonable production

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cost. However, after the millennium there have been some significant breakthroughs in

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the development of automation and land-based aquaculture technology (Drengstig and

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Bergheim, 2010b). Especially in the field of recirculation technology, major progress

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has made land-based aquaculture using heated water more economical realistic.

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Compared to other lobster species, the Homarus species are considered very hardy

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with a simple and abbreviated larval period. They feed readily on natural and artificial

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feeds (Drengstig et al., 2009), are resistant to disease and exhibit a very rapid and

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accelerated growth in warmed water (van Olst et al., 1980; Kristiansen et al., 2004).

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Thus, temperature is the primary controller of growth and optimum water temperature

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has been found to be 20oC (e.g. Aiken and Waddy, 1995). Larval period in 20oC water

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is around 12 days (Waddy, 1988; Drengstig et al., 2009) compared to 35 days at 15oC

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(van Olst et al. 1980). Furthermore, H. gammarus can reach 250-300g (total length 210

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mm; carapace length 75mm) in 24-30 months as long as constant 20oC water is

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provided (Wickins and Beard, 1991; Kristiansen et al., 2004). The much higher growth 2

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rate at 20ºC is primarily a result of the eliminated winter growth inhibition allowing for

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year-round growth and moulting. Because of large growth variation and high losses due to cannibalism and injuries

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when kept communally, the cultured lobsters have to be kept in individual containers.

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Thus, the ideal system for rearing lobsters individually should be relatively inexpensive

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to construct and operate, simple to maintain, based on automatic feeding and self-

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cleaning of tank and cages, maintain ideal water quality conditions, use space in three

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dimensions, enable high densities, conserve water at high temperatures, ensure good

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survival and permit easy access to the livestock for inspection and feeding (Aiken and

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Waddy, 1995). Aiken and Waddy (1995) reported that no successful attempts had been

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made which incorporated all of these features into a single design. Several different

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methods have been developed for culturing lobsters individually. All of them attempt to

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provide a separate compartment for each lobster, a constant supply of oxygen saturated

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seawater to each individual, a method of providing food and removing solids and

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dissolved wastes, and in general create an environment that will promote rapid, uniform

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growth and high survival (van Olst et al., 1980; Grimsen et al. 1987). Bottlenecks for

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commercial culture of lobsters have also been lack of high quality dry feed and

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technology that can solve the problems related to rearing in individual containers in an

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effective and profitable way (Drengstig and Bergheim, 2010b).

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Successful industrialization of land-based RAS farming has been warranted by

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overcoming the many technical challenges related to adopting the highly cannibalistic

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European lobster to high-tech profitable production technologies while still providing

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optimum rearing conditions. A major R&D project was conducted on the island Kvitsøy

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in SW Norway by Norwegian Lobster Farm Ltd. during 2000 – 2007. As a result, the

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company is today the only producer of European lobster in the world. The production

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utilizes a profitable land-based technology based on re-circulation of seawater and a

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world-wide patented single cage technology. The R&D program included testing of 6

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different technical solutions, developing a formulated diet fulfilling nutritional

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requirements, developing various automated solutions (feeding robot, harvesting robot,

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selection robot, remote desktop solutions, and image processing program), developing

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biological protocols, and conducting culinary tests and market studies. As a result,

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Norwegian Lobster Farm has managed to close the production cycle from egg to plate-

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size solely based on a formulated diet, demonstrating commercial harvests and market

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success both in terms of product quality and high farm gate prices. This paper presents 3

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the system design for the technology developed by Norwegian Lobster Farm and the

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how the system performed under commercial conditions. The biological data have been

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collected from a number of individual tests over the last 10 years.

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tank with an annual production capacity of 2 MT plate-sized lobsters (Figure 1 A). The

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farm was equipped with sea water pumps, mechanical water filtration units, UV filters,

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recirculation systems with biofilters, titanium heat exchangers, heaters, header tanks,

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rearing tanks, larval incubators and accessories. Moreover, the buildings were insulated

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to prevent heat loss. The total water volume of the hatchery was 30 m3 and the on-

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growing tank contains about 150 m3. Back-up water was taken from a depth of 52 meter

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below sea level.

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The construction consisted of a hatchery, a brood-stock section and an on-growing

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System design

Three recirculation loops supplied 300 L/min of filtered (mesh size: 30 μm) and aerated seawater of 18 – 20ºC. To each loop, 15 L/min of filtered and UV treated

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seawater was supplied the pump sump. The main units for water treatment were biofilter

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(aeration/flushing), screening filter and header tank for water chemistry stabilisation.

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The fluidized bed bio-filters were heavily aerated by air ejectors driven by the

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recirculation pumps. The size of the biofilters was 0.5 m3 filled with AnoxKaldnesTM

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biofilter media from KrügerKaldnes Ltd. up to 60% of the total volume of the biofilter.

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The filter media had an area-volume ratio of 500 m2/m3. UV-treated seawater was added

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corresponding to approximately one complete renewal of seawater in each loop every

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third day. The water exchange rate was temporarily been higher than this, especially in

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the early stages of testing out the RAS technology.

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The hatchery had an average production capacity of 350,000 IV stage juveniles annually

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using 24 upstream Kreisl incubators (40 L). The density during the pelagic stage (I-IV

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stage) was approximately 2,500 juveniles per incubator. A selection robot was used to

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determine when the larvae reached IV-stage. In this process, an image of each larvae in

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the incubator was captured, analyzed and its features were extracted and finally

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classified. The result of the final classification gave one of two possibilities; either the

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juvenile had reached IV-stage or not. The capacity was approximately 20 juveniles per

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minute. Juveniles between I-III stages were automatically transported back to their

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siblings in the incubator, while IV-stage juveniles were transported to a new robot in

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charge of distributing one lobster into one cage for on-growing.

143 In the on-growing facility, the single cages (Figure 1 B) rotated similar to conventional

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conveyer belts, and the lobsters were fed when the cages were in an up-right vertical

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position. The cameras were fixed under the feeding robots, enabling the system to

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monitor each single individual every day by taking pictures inside the cages before

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feeding. Image processing programs then determined whether the lobsters were dead or

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alive, and if moulting had occurred. The image processing program also extrapolated

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the expected time to harvest by calculating moulting frequency. After feeding, the cages

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rotated in right hand direction, and new cages came into vertical up-right position.

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Lobsters inhabiting the cages on the way down started eating their daily meals. When

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the cages came in vertical down-wards position, uneaten feed and fecal waste fell out of

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the cages. A wiper with suction rotated vertically on the bottom, efficiently cleaning the

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tank floor. Self-cleaning of cages was facilitated by inlet current flow being placed

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within each single-cage unit, while outlet current flow was positioned between the units.

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Thus, new water was supplied every single cage in addition to providing a slightly

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overhead pressure pushing the waste out of the cages facing down towards the bottom.

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A principal sketch of the patented technology is presented in Figure 1 B and Figure 1 C

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shows the technology in operation.

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Figure 1 A

Figure 1 B

Figure 1 C

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The stocking densities varied according to individual size, with maximum biomass of

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25 kg/m3 for 6 cm lobster, 35 kg/m3 for 12 cm and approximately 45 kg/m3 for portion

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sized lobsters, respectively.

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3.

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length (TL) were measured during the initial trials at Kvitsøy. However, calculations

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showed a consistent ratio between CL and TL with a correlation of 0.97 and, thus, only

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CL was measured in the present study (Kristiansen et al., 2004). The time needed to

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produce a 300g lobster (approximately 75 mm CL) is dependent on growth rate. In the

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RAS setup at Norwegian Lobster Farm, portion sized lobsters are produced from

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hatching to 300g within 800 to 900 days or approximately 17,000 day-degrees at

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favorable conditions (Drengstig et. al 2009). In Figure 2 linear growth lines have been

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extrapolated based on obtained growth results Kvitsøy (Kristiansen et al. 2004). The

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growth of the lobsters produced in this RAS system equals the best growth rates

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published from other studies (e.g. Wickins and Beard, 1991; Waddy, 1995).

System performance

3.1. Growth and feed utilisation

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In order to determine growth rates of lobsters, both carapace length (CL) and total

As already demonstrated in several individual trials, it is not unrealistic that plate-

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sized lobsters can be mass-produced from IV stage to 300g in less than 24 months under

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intensive production levels (Kristiansen et al., 2004; Drengstig et al., 2009). A

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prerequisite to obtain such production time is however using an optimum diet and

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feeding regime, and keeping a stable environment in the system. Moreover, by using the

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new formulated lobster feed (Table 1), all individuals maintained a natural black color.

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On the other hand, lobsters fed traditional marine fish feed available on the market

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turned pale blue to white after 2-3 moults. Three different astaxanthin levels were tested

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(50, 100 and 200 mg/kg dry weight), but no variation in pigmentation was observed

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between the three levels (Drengstig et al. 2003). The average feed conversion ratio

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(FCR) was approximately 1.5 under commercial scaled production, whereas FCR were

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1.2 -1.3 under small scale controlled trials.

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In addition, selection of family groups with fast growth under intensive farming

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conditions could further reduce the production time. Several studies have been

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performed at Kvitsøy in order to promote year-round hatching and reveal correlations

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between the quality of the female lobster and the egg quality in terms of growth and

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survival rate (Agnalt, 2008; Drengstig et al., 2011).

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Figure 2

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Table 1

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3.2.

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obtain good welfare and growth, and reduce stress and risk of disease outbreaks.

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Especially in closed recirculation systems, where there is little or no exchange of water,

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a build-up of toxic metabolites and reduction in oxygen concentrations may happen very

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rapidly (Timmons and Losordo, 1994). However, in land-based profitable lobster

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farming, re-circulation of water is necessary to reduce heating costs. Thus, in any

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occasion, it is important to understand what the optimal as well as limiting culture

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conditions are for lobsters.

Water quality

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A system that supplies water of good quality is an essential factor if we want to

Oxygen supersaturated water has on the other hand been shown to cause serious

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damage as gas bubbles can develop in the hemolymph and restrict blood flow (Aiken

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and Waddy, 1995). Furthermore, while lobster may tolerate wide fluctuations in

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salinity, optimal conditions ranges between 28 – 35 ‰ (van Olst et al., 1980; Richards,

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1981; D’Abramo and Conklin, 1985). Whilst Beard et al. (1985), Beard and McGregor,

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(2004), and Jacklin and Combes (2007) were unable to provide recommended limits for

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nitrite and nitrate, ammonia concentration is most likely the most limiting water quality

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parameter in recirculation systems for seawater. Although the optimal TAN

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concentration given by van Olst et al. (1980) is slightly higher than that recommended

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by D’Abramo and Conklin (1985) of less than 1.5mg/l, there is no doubt that Homarus

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sp. are more tolerant than most finfish. Estrella (2002) indicated that short-term

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acceptable levels of nitrite and nitrate might be as high as 5 mg/L and 100 mg/L,

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respectively. According to Wickins and Lee (2002), the desirable levels of water quality

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for clawed lobsters are temperature of 18 – 22 ºC, salinity of 28 – 35 ‰, above 6.4 mg

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oxygen/L, pH of 7.8 – 8.2 and less than 14 μg N/L as un-ionized ammonia. Thus, it

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seems like European lobster can, for short periods, tolerate considerably lower oxygen

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and higher ammonia concentrations than indicated as desirable levels.

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Available literature of metabolic rate in European lobster is sparse but Hamelo

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(2006) performed some studies at Kvitsøy and measured strongly fluctuating oxygen

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consumption in lobster of different size at 19ºC:

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Small/fry

7 – 10 g:

0.8 – 6.3 mg O2/kg x min

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Medium-size

43 - 54 g:

0.5 – 3.5

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Large

0.7 – 2.1

148 - 208 g:



247 The large individual variability in oxygen consumption at various sizes also

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demonstrates rapid adaptability to new conditions. Typical stress influenced respiration

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rate seems to be approximately twice the standard rate. The standard rate of European

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lobster within the size interval 230 – 600 g was found to be 0.73 mg O2/kg x min at 20

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°C (Whiteley et al., 1990), i.e. about half of the lowest rate found for lobster of 208 g

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farmed at Kvitsøy.

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The oxygen consumption ranges were large, 1:8 to 1:3 within the same size groups,

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and the fluctuations were due to diurnal rhythm and peaked at feeding (Hamelo, 2006).

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The measured CO2-production was on average 1.5 – 2 times the corresponding O2-

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consumption.

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A smaller follow-up study was conducted at the International Research Institute of

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Stavanger (IRIS) in 2010 (Figure 3). Some of the animals were obviously temporarily

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stressed, and peak rates were always measured during the first monitoring. In addition,

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several of the adults, i.e. the individuals of 93.9 g, 122 g and the largest one of 208 g,

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seemed to suffer from stress in the respirometer, probably due to the small size of the

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chamber. Figure 3

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Excretion rates were also measured during the respirometer study performed by IRIS

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in 2010. The ammonia analyses indicate, as expected, a higher specific excretion rate in

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terms of mg TAN/kg x min in fry compared to in larger animals:

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Small/fry

0.5 – 1.8 g:

0.35

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Medium sized

20 – 44 g:

0.07 – 0.1



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Large

94 – 208 g:

0.04 – 0.09



mg TAN/kg x min

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However, replicate sampling of the same size groups demonstrated considerable

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fluctuation from one test situation to another. Increased excretion rate in the largest

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animals (122 - 208 g) was positively correlated with increased oxygen consumption in

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the same individuals. Beard et al. (1985) estimated excretion rates in adults (H.

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gammarus L. of 300 g) of 0.10 – 0.37 mg TAN/kg x min or up to 3 – 4 times the rates

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found in the present test (size: 208 g). 8

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At Kvitsøy, the biofilter is efficiently removing total ammonia (TAN) at average rates

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of 50 – 70% of the before – after biofilter concentration. Concentration of un-ionized

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ammonia (NH3) as per cent of total ammonia nitrogen (TAN) was calculated according

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to the following equation:

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% NH3 = 100 / (1 + antilog (pKa – pH))

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where the dissociation constant, pKa, ranges from 9.09 to 9.90 dependent on

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temperature and salinity (Alabaster & Lloyd 1982).

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Lobster feed is high in protein and the ammonia excretion rates in the animals are

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correspondingly high with average rates of 0.1 – 0.5 g TAN/kg x day reported for adult

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lobster. Due to the high protein content of the feed and the reported low tolerance to

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ammonia (Wickens and Lee, 2002), the efficiency of the biofilter is vital in RAS for

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lobsters (e.g. Crear and Forteath, 2002). Table 2

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At low loading level in the grow-out pilot, all measured parameters were within or

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slightly outside the desirable range for lobster (Table 2). The concentration of unionized

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ammonia (NH3) of 32 µg/L was lower compared to sampling before and after the actual

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date. Besides, the embedded biofilters seemed to work rather well, stable and problem

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free at a loading level of 0.1 kg/m3 per 24 hours (Drengstig and Bergheim, 2010a).

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Ongoing extended water sampling of the present system with higher biomass and

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correspondingly increased loading level will provide more basic criteria for optimizing

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the management of RAS for commercial production of European lobster.

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4.

Conclusion Currently there is still a lack of knowledge on respiration and excretion rates of

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lobster at all stages, and documentation of optimum rearing conditions in RAS. Based

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on the economic importance of these issues, priority should be given to detecting critical

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water quality values for dimensioning of technical equipment in order to sustain a

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healthy environment for the biomass. Moreover, it is important for successful

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commercialization to improve growth performance, survival and feed conversion ratio

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(FCR) in RAS in order to increase the turn-over in the biomass. Feed development and

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genetic breeding is of course essential factors for improved growth rates in land-based

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lobster aquaculture. References

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Agnalt, A.-L., 2008. Stock enhancement of European lobster (Homarus gammarus) in Norway; Comparisons of reproduction, growth and movement between wild and cultured lobster. Dr. scient. thesis, Department of Biology, University of Bergen, Norway.

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Alabaster, J. S., Lloyd, R., 1982. Water Quality Criteria for Freshwater Fish. FAO, Butterwords, London. 2nd Ed. 361 p.

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Aiken, D. E., Waddy, S. L., 1995. Aquaculture. pp. 153-175. In: Factor, J. R. (Ed.), Biology of the lobster Homarus americanus. Academic Press, Inc.

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Beard, T. W., McGregor, D., 2004. Storage and care of live lobster. Laboratory leaflet number 66 (revised). Cefas. UK. Beard, T. W., Richards, P. R., Wickins J. F., 1985. The techniques and practicability of year-round production of lobsters, Homarus gammarus (L.), in laboratory recirculation systems. Fisheries Research Technical Report, No. 79, Lowestoft, UK. ISSN 0308 – 5589. 22 p.

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Crear, B. J., Forteath, G. N. R., 2002. Feeding rate has the largest effect on the ammonia excretion rate of the southern rock lobster, Jasus edwardslii, and the western rock lobster, Panulirus cygnus. Aquacultural Engineering 26, 239 – 250.

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Coffelt, R. J., Wikman-Coffelt J., 1985. Lobsters: One million One Pounders per Year. Aquacultural Engineering 4, 51 – 58. D’Abramo, L. R., Conklin, D. E., 1985. Lobster aquaculture. In: Huner, J., Brown, E.E. (Eds.), Crustacean and mollusc aquaculture in the USA. AVI Publ. Co., Westport, Conn., USA, pp. 159 – 201. Drengstig, A., T. S. Kristiansen, A. Bergheim, T. Drengstig & L. Aardal (2003). It does matter if they are black or white! Quantification of the minimum required level of astaxanthine to ensure natural pigmentation in the European lobster. pp 168 – 169. Extended abstract and Poster presentation. EAS special publication No. 33. August 2003. Trondheim, Norway. 408 pp. Drengstig, A., Drengstig, T., Agnalt, A.-L., Jørstad, K., Farestveit, E., 2009. Utvikling av metoder for stabil produksjon av hummeryngel med gode vekstegenskaper. 42 p. [In Norwegian] (http://www.rup.no/vision/vision7.aspx?hierarchyid=763&type=3)

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Drengstig, A., Bergheim, A., 2010a. Single cage technology for on-growing of lobster in RAS. Abstract and oral presentation, Progress in Marine Recirculating Aquaculture Systems – World Aquaculture Society, San Diego, California, USA, 1 – 5 March 2010. Drengstig, A., Bergheim, A., 2010b. A pilot RAS for commercial production of European lobster. Aquacultural Engineering Society Proceedings VII, pp. 178-186. AES Fifth Issues Forum, Roanoke, Virginia, USA, 16 – 20 August 2010.

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Drengstig, A., Agnalt, A.-L., Jørstad, K., 2011. Genetic mapping to improve growth performance, survival and feed conversion ratio (FCR) for on-growing of European lobster in Recirculating Aquaculture Systems (RAS). Proceeding 9th International Conference and Workshop on Lobster Biology and Management, Bergen, Norway, 19 – 23 June 2011.

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Estrella, B. T., 2002. Techniques for live storage and shipping of American lobster. Technical Report TR-8, 18. Division of Marine Fisheries, Massachusetts.

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Factor, J. R., 1995. Biology of the lobster Homarus americanus, Academic Press, Inc., New York. 528 p.

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Grimsen, S., Jaques, R. N., Erenst, V., Balchen, J. G., 1987. Aspects of automation in a lobster farming plant. Modelling, identification and control, 8 (1), 61 – 68. Hamelo, J. S., 2006. Investigation of respiration rates of European lobster (Homarus gammarus) in land-based, lobster farming system. Master thesis, Univ. of Stavanger, Norway. 86 p.

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Jacklin, M., Combes, J., 2007. The good Practice Guide to Handling and Storing Live Crustacea. http://www.seafish.org/media/Publications/CrustaceaGPG_0505.pdf

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Kristiansen, T. S., Drengstig, A., Bergheim, A., Drengstig, T., Svensen, R., Kollsgård, I., Nøstvoll, E., Farestveit, E., Aardal, L., 2004. Development of intensive farming methods for the European lobster (Homarus gammarus L.) in recirculated seawater. Results from experiments conducted at Kvitsøy Lobster Hatchery from 2000 to 2004. Fisken og Havet, 6 – 2004, Institute of Marine Research, Bergen, 52 p. ISSN 0071 – 5638. (http://www.imr.no/__data/page/3839/Nr.6_2004_Methods_for_intensive_farming_of_E uropean_lobster.pdf). Nicosia, F., Lavalli, K.,1999. Homarid lobster hatcheries: Their history and role in research, management, and aquaculture. Marine Fisheries Review 61(2), 1-57. Richards, P. R. 1981. Some aspects of growth and behaviour in the juvenile lobster Homarus gammarus (Linnaeus). PhD Thesis University of Wales, Bangor, Great Britain. 209 p. Timmons, M. B., Losordo, J. G., 1994. Aquaculture water reuse systems: engineering design and management. Elsevier, New York, USA. van Olst, J. C., Carlberg, J. M., Hughes, J. T., 1980. The biology and management of lobsters, pp. 333 -384. In Cobbs, J. S., Phillips, B.F. (Eds.), Aquaculture, Vol. II Academic Press, Inc., New York. 468 p. 11

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Waddy, S. L., 1988. Farming the Homarid Lobsters: State of the Art. World Aquaculture,19 (4), 61 – 71. Whiteley, N. M., Al-Wassia, A. H., Taulor, E. W., 1990. The effect of temperature, aerial exposure and disturbance on oxygen consumption in the lobster, Homarus gammarus (L.). Mar. Behav. Physio. 17, 213 – 222.

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Wickins, J.F., Beard, T.W., 1991. Variability in size at moult among individual broods of cultured juvenile lobsters. Aquaculture and Fisheries Management 22, 481 – 489.

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Wickins, J. F., Lee, D. O., 2002. Crustacean Farming – Ranching and Culture. Blackwell Science. 446 p.

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*Manuscript

Figure and Table captions:

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Fig. 1. RAS facilities at Norwegian Lobster Farm (NLF), Kvitsøy. A) Flow diagram and design of the hatchery, broodstock and grow-out sections with water treatment units B) Principle sketch of the single cage technology C) Fully automated production unit and tank system including, A) single cages, B) feeding robot, C) cameras and image processing solutions, D) control units and E) machine room in centre below deck.

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Fig. 2. Four estimated growth rates of European lobster from size stage IV until plate-size (75 mm CL). Squared and circular marks indicate measured growth at NLF.

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Fig. 3. Mean oxygen consumption of European lobster (individual size: 0.06 – 208 g) at 19.5 – 20.3 °C (Report IRIS, unpublished). Unit: mg O2/kg x min.

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Table 1 Chemical composition and nutritional content of the feed.

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Table 2 Water quality at four sampling points at low loading level in the grow-out unit, NLF, November 2004.

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Figure 1 A

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Figure(s)

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Figure(s)

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Figure(s)

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B) Feeding robot

C) Cameras

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A) Single cage farming units

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D) Control units

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Figure 1 C

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E) Machine room below deck

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Figure(s)

0.10 mm/day

70

0.09 mm/day 0.08 mm/day

60

0.07 mm/day goal Kvitsøy small

40

Kvitsøy large

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CL(mm)

50

30

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20

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10 0 90

180 270 360 450 540 630 720 810 900 990 1080

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Figure 2

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Days from Stage IV

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Figure 3

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Table(s)

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Nutrient content % of wet weight Protein 54.7 Lipid 15.6 Carbohydrates 13.6 Ash 9.5 Moisture 6.8 Crude energy (MJ/kg) 21.6 Astaxanthin level was 50, 100 and 200 mg/kg dry weight.

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ip t cr Salinity ‰ 8.30 33.7 8.15 33.6

6.4 (89) 6.4 (89)

S-DM, mg/L <5

TOC, mg/L 2.2

TAN, µg/L 645

5.3 6.4

3.2 -

29 -

NH3-N*, µg/L 32 <5 -

NO3-N, µg/L 1,880

Flow L/h 90 6,000

1,860 -

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Make-up water Outlet lobster tank Outlet biofilter 18.4 8.32 33.5 Outlet drumfilter 18.4 8.32 33.6 *: Calculated (Alabaster and Lloyd, 1982)

DO, mg/L (%) 8.3 (92) 6.2 (82)

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pH

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Temp. °C 10.0 18.2

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Table 2 Sampling point

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Salinity ‰ 8.30 33.7 8.15 33.6

6.4 (89) 6.4 (89)

S-DM, mg/L <5

TOC, mg/L 2.2

TAN, µg/L 645

5.3 6.4

3.2 -

29 -

NH3-N*, µg/L 32 <5 -

NO3-N, µg/L 1,880

Flow L/h 90 6,000

1,860 -

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Make-up water Outlet lobster tank Outlet biofilter 18.4 8.32 33.5 Outlet drumfilter 18.4 8.32 33.6 *: Calculated (Alabaster and Lloyd, 1982)

DO, mg/L (%) 8.3 (92) 6.2 (82)

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Table 2 Sampling point

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Table(s)

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