Textile substrate seeding of Saccharina latissima sporophytes using a binder: An effective method for the aquaculture of kelp

Textile substrate seeding of Saccharina latissima sporophytes using a binder: An effective method for the aquaculture of kelp

Algal Research 33 (2018) 352–357 Contents lists available at ScienceDirect Algal Research journal homepage: www.elsevier.com/locate/algal Textile s...

1010KB Sizes 1 Downloads 32 Views

Algal Research 33 (2018) 352–357

Contents lists available at ScienceDirect

Algal Research journal homepage: www.elsevier.com/locate/algal

Textile substrate seeding of Saccharina latissima sporophytes using a binder: An effective method for the aquaculture of kelp

T



Philip D. Kerrison , Michele S. Stanley, Adam D. Hughes SAMS, Scottish Marine Institute, Oban, Argyll PA37 1QA, UK

A R T I C LE I N FO

A B S T R A C T

Keywords: Saccharina latissima Seeding Sporophyte Cultivation Textile Substrate

The macroalga Saccharina latissima holds promise as a widespread crop in northern Europe. Currently, seeded lines are cultured for 1–2 months within a hatchery until they become ≥1 mm sporophytes, which are then outplanted to a farm. Textiles are being developed as a cultivation substrate for macroalgae, however due to their large surface area, these need either direct in-situ seeding at the farm or a very short, high turnover hatchery period. Two materials, Kuralon twine and non-woven textile, were seeded using three S. latissima developmental stages: meiospore, gametophyte or juvenile sporophyte. The gametophyte and sporophyte stages were applied using a binder solution to adhere them to the materials. These were outplanted at a seaweed farm in the Sound of Kerrera, UK. After 5 weeks, fronds were significantly larger (45 ± 25 mm) and more abundant (20 ± 8·20 cm−1) when seeded with sporophytes over gametophytes or meiospores (8 ± 10 mm and 2 ± 2·20 cm−1). This reflects the growth advantage of outplanting juvenile sporophytes, since they are larger and more developed when outplanted. Higher fouling of filamentous algae was seen on the non-woven textile but this did not appear to affect growth. After four months, sporophyte seeded materials had the largest fronds and the greatest fresh mass of 2.1 ± 0.8 kg·20 cm−1, equivalent to simultaneously deployed hatchery reared twine (2.0 ± 0.1 kg·20 cm−1). Gametophyte seeding achieved 0.8 ± 0.6 kg·20 cm−1 while meiospore seeding achieved only 0.1 ± 0.1 kg·20 cm−1. No difference was found between growth on Kuralon twine or non-woven textile (p > 0.05), showing that both are suitable growth substrates. Seeding of juvenile sporophytes onto textile using the binder is demonstrated to be a successful method for the cultivation of S. latissima, and may require only 1% of the hatchery tankage, once optimised. It is expected that this method is transferable to the cultivation of other kelp species.

1. Introduction The macroalga Saccharina latissima (Phaeophyceae) is a fast growing subtidal European kelp, which develops from a 8–10 μm meiospore into a 1.5–2 m adult within a single year [1,2]. It is commonly found in shallow, low to moderately wave disturbed subtidal marine environments where it acts as an ecosystem engineer providing a habitat for a range of other species [3,4]. There is continuing research into S. latissima cultivation across Europe [5–7], which should limit environmental damage or degradation associated with harvesting of natural beds [4,8]. Cultivated kelp has value as a human food [9], animal feed [10], nutrient absorption and an additional income stream as part of integrated multi-trophic aquaculture [6,11,12]. Kelps are also a focus of research into mass cultivation as a biofuel or for carbon sequestration due to their high carbohydrate content [13–15]. Single-celled haploid meiospores are released from the sorus of adult sporangial tissue of kelp; these settle and develop into either male ⁎

or female gametophytes. Fertilisation leads to the development of new diploid sporophytes which then grow to adult size [16]. For cultivation, released meiospores or gametophyte cultures are settled or sprayed onto twines which are cultured in indoor hatcheries for 1–2 months [5,17]. This minimises competition and prevents grazing, allowing the successful development of sporophytes for transfer to the open sea (when ≥1 mm) without competition from other settling organisms. Textile sheets have been suggested as growth substrates for the large scale sea cultivation of macroalgae, and are known to be suitable for the attachment of kelp species [18,19]. However, their large size would make the hatchery phase unfeasible. Consequently, for textile sheets to be a viable substrate, either a very short hatchery time or direct in-situ seeding is required. The aims of this study are: 1) To compare three methods of direct seeding of S. latissima; using either meiospores, gametophytes or sporophytes;

Corresponding author. E-mail addresses: [email protected] (P.D. Kerrison), [email protected] (M.S. Stanley), [email protected] (A.D. Hughes).

https://doi.org/10.1016/j.algal.2018.06.005 Received 14 August 2017; Received in revised form 24 May 2018; Accepted 2 June 2018 2211-9264/ © 2018 Elsevier B.V. All rights reserved.

Algal Research 33 (2018) 352–357

P.D. Kerrison et al.

c) a)

b)

2 cm 20 cm Fig. 1. Photograph of the a) 6 mm ø Kuralon twine and b) non-woven textile used in this study. c) Prepared line during transit to deployment site. All pre-seeded materials were cable tied into position in a randomised order every 20 cm.

sporophyte·mL−1. 2.75 mL was found to be the maximum volume of this suspension that could be soaked into 30 cm of Kuralon twine. This volume was spread evenly across the surface of the non-woven textile to standardise the seeding density. Both materials were prepared in triplicate and left for 30 min in the air. These were then submerged in 2 L tanks of F/2-Si. Concurrently, meiospores were extracted from five further pieces of S. latissima from the same location. One million extracted meiospores were placed into a 2 L tank of F/2-Si containing both materials, in triplicate. The estimated settlement density was 2500 meiospores·cm−2. The tanks were then incubated for 3 d at 8.5 °C and 5–10 μmol photon·m−2·s−1, 12:12 L:D. For deployment, the test materials were attached using cable ties onto a polyester rope (8 mm ø; Bexco NV-SA, BE) in a randomised order at 20 cm intervals. The 30 cm sections of Kuralon twine were wrapped around a 20 cm length of rope, the same as the non-woven textile. The line was reeled and wrapped in plastic to prevent dehydration or rain exposure during transport (Fig. 1c). The line was deployed on 28th February 2014 suspended at ca. 1.5 m depth at the Sound of Kerrera experimental seaweed farm, Scotland (56.3820°N, −5.5370°E). As an additional comparison, 30 m of twine was seeded with meiospores of S. latissima and grown using traditional hatchery techniques (Kerrison et al. 2016) until a dense coverage of 1–3 mm sporophytes were present after 8 weeks. These were outplanted at the same time as the experiment above.

2) Determine if textiles are a suitable cultivation substrate for S. latissima by comparing growth on both Kuralon twine and a nonwoven textile. 2. Materials and methods 2.1. Material preparation Braided Kuralon twine (6 mm ø; Tecnored, ES) was cut into 300 mm sections. Non-woven textile (Sioen Industries NV, BE; Sioen Industries NV 2013) was cut into 200 × 45 mm sections, which were folded and sewn along their width (Fig. 1). Both materials were soaked in 5% Decon90 for 24 h to remove manufacturing residues, then rinsed and left to soak in distilled water for 24 h, before finally oven dried at 40 °C. 2.2. Culture preparation and seeding of materials Five fertile S. latissima were collected from Seil Sound, UK (56.31724°N, −5.58309°E). The sporangial regions were excised and wiped multiple times with laboratory tissues (Kimtech, UK) and Tyndallised seawater to remove epiphytes [20,21]. The sporangial regions were then left to partially dehydrate overnight in a refrigerator at 4 °C, then rehydrated in 8.5 °C Tyndallised seawater enriched with F/2 medium without silicate (F/2-Si) for 1 h, in the dark to induce meiospore release [17]. The meiospore suspension was filtered through 50 μm mesh, divided into two 2 L flasks and cultured in bubbled F/2-Si at 8.5 °C and 40–50 μmol photon·m−2·s−1, 12:12 L:D. The density of the culture was in the region of 500,000 cell·L−1. Germanium dioxide (0.125 mL saturated solution·L−1) was also added during the first two weeks of cultivation to prevent diatom contamination [17]. One flask was cultured under red light to prevent gametophyte fertilisation, while the other was cultured under white light to promote fertilisation and sporophyte development. Every 10–14 d, the culture was allowed to settle and half the media decanted and refreshed. Attached gametophytes/sporophytes were gently re-suspended with a sterilised nylon brush. Once the largest sporophytes reached 1–2 mm (after ca. 6 weeks), the gametophyte flask was transferred into white light and after five days, oogonia formation was evident. Both cultures were brought to the same concentration and mixed with a 1% binder solution (AT~SEA Technologies, BE), creating a concentration of 330 gametophyte/

2.3. Site visits After five weeks, the lines were inspected. Photographs were taken of a 10 cm section of each substrate. From these photographs, the % cover of fouling filamentous algae was estimated by eye, the number of apparent sporophytes were counted and the length of the five largest fronds were measured using ImageJ software v1.46r. After four months, all the lines were retrieved and all sporophytes were counted, measured and their combined mass recorded. 2.4. Statistical analyses The Anderson-Darling test for normality [22] was applied to all data. Where this was satisfied a two way ANOVA (2wAN) was conducted. If this was not the case a Kruskal Wallis test (KW) was used. 353

Algal Research 33 (2018) 352–357

Mean frond length (mm)

P.D. Kerrison et al.

80 60 40 20 0

M

Sporophyte (·20 cm-1)

40

G

S

M

G

S

b)

30

3.2. Four month timepoint After 4 mo, the number of sporophytes was not affected by the substrate material (p > 0.05; Fig. 3b) but was significantly affected by the seeding method (2wAN: F1,2,2,12 = 21.2, p < 0.0001). The meiospore seeded treatment had an average 0.7 ± 0.6 sporophyte·20 cm−1 and was significantly different from the other treatments (AN F1,10 = 12.8–31.4, p < 0.01). The gametophyte and sporophyte treatments were not different (p > 0.05) with an average of 45 ± 27 sporophyte·20 cm−1. The mean maximum length of the fronds (Fig. 3a) was also not significantly different between the materials (p > 0.05) but was significantly different between seeding methods (2wAN: F1,2,2,12 = 67.3, p < 0.001), with each combination significantly different from the others (AN: F2,10 = 11.4–162, p < 0.001). The mean maximum length of fronds in each treatment was 3 ± 3, 55 ± 11 and 87 ± 16 cm for meiospore, gametophyte and sporophyte, respectively. The biomass yield of S. latissima (Fig. 3c) was not significantly different between the two materials (p > 0.05), although it was significantly different between the seeding methods (2wAN: F1,2,2,12 = 18.2, p < 0.0001) and this was clearly visible on photographs (Fig. 4). The mean yield for the meiospore, gametophyte and sporophyte seeding treatments were 0.1 ± 0.1, 0.8 ± 0.6 and 2.1 ± 0.8 kg·20 cm−1, respectively. By comparison, the line seeded using traditional hatchery twine achieved 2.0 ± 0.1 kg·20 cm−1, not significantly different from the sporophyte seeded treatment (p < 0.05). The frequency distribution of frond length after 4 months was examined for the gametophyte and sporophyte treatments, and were found to be significantly different (KS: D241/205 = 0.36–0.37, p < 0.0001; Fig. 5). A more even distribution was seen when sporophyte seeding, due to a greater frequency of larger fronds: When gametophyte seeded, only 2–6% of fronds were ≥80 cm, whereas this was 19–26% when sporophyte seeded. In both cases, the median size class was 20–40 cm, which composed 45% of the population for gametophyte seeded, but only ~30% for sporophyte seeded. The material choice made no difference to the frequency distribution (p > 0.05).

20 10 0 M

100

Fouling cover (%)

with 45 ± 25 mm fronds (AN: F1,10 = 14.1–16.0, p < 0.005). No difference in frond length was seen when comparing the Kuralon and nonwoven textile (p > 0.05). The density of apparent sporophytes (Fig. 2b) followed the same pattern as the mean frond length. A significant difference was found between seeding treatments (2wAN: F1,2,2,12 = 21.2, p < 0.0001). The meiospore and gametophyte treatments had means of 2–3 sporophyte·20 cm−1 and were not significantly different (p > 0.05). The sporophyte treatment was significantly different to both (AN: F1,10 = 35.4–40.1, p < 0.0001), with 20 ± 8 sporophyte·20 cm−1. Again, no difference was found between the Kuralon and non-woven textile (p > 0.05). The % cover of fouling was significantly different between the two materials (MW: d.f. = 9,9, p < 0.05). Kuralon had a mean fouling coverage of 49 ± 6%, while the non-woven textile had a mean of 81 ± 13%. The fouling cover was not affected by seeding treatment (p > 0.05).

a)

G

S

M

G

S

c)

75 50 25 0

Fig. 2. Saccharina latissima sporophyte a) mean frond length, b) density and c) fouling cover, 5 weeks after seeding. Comparison of three developmental stages seeded onto two different substrates: M = meiospore, G = gametophyte, S = juvenile sporophyte < 2 mm, white columns = Kuralon twine, grey columns = non-woven textile. Shown is mean ± standard deviation (n = 3).

Where only one variable (material/seeding method) showed significance, the data from the non-significant variable was pooled for further comparisons. Significant results were tested using either pairwise one way ANOVAs (AN) or Mann-Whitney U tests (MW). The frequency distribution of frond length was analysed using pairwise Kolmogorov-Smirnov tests (KS).

4. Discussion 3. Results Textiles have been proposed as a substrate for the cultivation of macroalgae as their chemistry and structure can be manipulated to maximise attachment, and they provide versatility to create new structures which may allow optimal sea space usage [23]. Textiles have already been shown to be suitable substrates for the attachment of Laminaria digitata in tanks, with increased rhizoid production due to their microscopic roughness, and the creation of an enmeshed holdfast structure as the rhizoids envelop the fibres [18]. This study has found

3.1. Five week timepoint The mean length of the five largest fronds (Fig. 2a) was significantly different between the seeding methods (2wAN: F1,2,2,12 = 9.3, p < 0.005). No significant difference was found between the meiospore and gametophyte treatments (p > 0.05), with mean lengths of 3–13 mm. The sporophyte treatment was significantly different to both 354

Algal Research 33 (2018) 352–357

Development stage seeded

100

Gametophyte

75

Kuralon twine

25 0 M

G

S

M

G

S

b)

75 50

50 cm

25 0 M

Fresh mass (kg·20 cm-1)

Sporophyte <2 mm

50

100

Sporophyte(·20 cm-1)

Meiospore

Non-woven texle

Mean frond length (cm)

P.D. Kerrison et al.

4.0

G

S

M

G

S

c)

3.0 2.0 Fig. 4. Photograph of median growth response of Saccharina latissima after four months. Comparison of three seeding methods and on two substrates.

1.0 0.0

Fig. 3. Saccharina latissima sporophyte a) mean frond length, b) density and c) fresh mass, 4 months after seeding. Comparison of three developmental stages seeded onto two different substrates: M = Meiospore, G = gametophyte, S = juvenile sporophyte < 2 mm, white columns on left = Kuralon twine, grey columns on right = non-woven textile. Shown is mean ± standard deviation (n = 3).

% of population

50

that in the sea, a non-woven textile was just as effective as commercially available Kuralon twine for the cultivation of S. latissima. It was also found that in the early stages of growth, fouling by filamentous algae such as Ectocarpus spp. was enhanced on the non-woven. However, this did not appear to affect the growth of S. latissima. A primary practical issue impeding the use of textiles for macroalgal cultivation is how to seed them. Generally for kelp cultivation, Kuralon twine is wound onto reels, or other structure, seeded and allowed to grow in a hatchery over many weeks until well attached sporophytes have developed [5]. The twine can then be unfurled onto a length of rope. High surface area textiles sheets cannot be seeded using this hatchery method, without an excessively large areal tankage requirement. For the commercial use of textiles in macroalgal cultivation, they therefore require a method that requires either a very short hatchery time (i.e. days), or allows direct in-situ seeding of the material.

Sporophyte

25 Gametophyte 0

Length (cm) Fig. 5. Saccharina latissima population structure, 4 months after seeding. Comparison of seeding with two developmental stages (gametophyte and sporophyte) onto two different material substrates: light grey columns = Kuralon twine, dark grey columns non-woven textile.

This study has investigated direct seeding using different growth stages of S. latissima. A commercially secret binder (AT~SEA Technologies, BE) was used to thicken suspensions of both gametophytes and sporophytes, which were then applied to the test materials, preventing the suspended macroalgae from being washed off before they can attach. Motile meiospores were separately allowed to settle 355

Algal Research 33 (2018) 352–357

P.D. Kerrison et al.

conditions needs to be conducted to test this hypothesis.

onto test materials for 3 d, without the binder. This gave them the best opportunity for adhesion, as using the binder would have reduced the number in contact with the material surface. The binder method can allow seeded materials to be immediately placed in the sea resulting in successful growth (Kerrison et al. in prep). However in this study, a 3 d settlement period was allowed as the authors felt that immediate submersion would have biased the results against the meiospores, washing them away before they could settle. The results show that binder seeding is a successful method to seed using either gametophytes (20–50 μm) or sporophytes (0.5–2 mm) leading to a sporophyte density of ca. 450 m−1 on both materials, a tenth of the initial seeding density (4540 m−1). However, only 19–25% of these developed into fronds > 80 cm in the sporophyte seeded treatment, with 30% still < 20 cm. This indicates substantial intraspecific competition, with larger fronds suppressing the growth of their smaller compatriots [24]. A lower initial seeding density could lead to a more even population distribution. Overall, seeding using sporophytes provided a growth advantage over gametophytes: growing larger fronds and achieving twice the biomass after 4 months. This method can therefore be used to A) increase the final biomass achieved and/or B) reduce the cultivation time needed to reach a required size. This is to be expected, given the ~2–3 weeks more advanced development of the seeded sporophytes compared to the gametophytes [17]. Binder seeding using sporophytes achieved in similar biomass to the traditional twine method, but with further optimisation, may hold considerable advantages over the traditional method including A) the binder method could be easily automated and applied over large surface areas simultaneously, whereas the twine method requires time-consuming wrapping of individual lines. B) The method may allow fast seeding onto a wide variety of cultivation substrates, including two/three-dimensional structures, as well as traditional 1D ropes. 3) The volume of tankage required to produce sporophyte tumble culture is far below that required for a twine hatchery. i.e. The SAMS hatchery produces 1 km of seeded twine in 87 L of tankage, while the cultivation manual of Flavin et al. was calculated to use 150 L [25]. By comparison, sporophyte culture and seeding using the methodology of this study (non-optimised), would require < 2 L of culture to seed 1 km. This means that a hatchery based around sporophyte-binder seeding may be in the order of 100 times as space efficient as a twine-based hatchery. The purpose of the binder is not to permanently glue the sporophyte/gametophyte onto the substrate, as this could encase them, causing suffocation or preventing growth. Instead, the binder brings them into close enough proximity so that they can develop a holdfast attachment. The high viscosity of the binder solution prevents the sporophyte/gametophyte from being washed away immediately, while the binder itself remains in place over the timescale of more than a week (pers. obs.). Therefore, the binder suspended gametophyte/sporophyte, has this limited time period in which to develop a holdfast attachment to the substrate material. It is expected that a large proportion of the juveniles are washed away at this stage, as their holdfasts are, by chance, oriented so that they are not able to contact the surface before the binder degrades. A rough texture, such as the non-woven textile, may lead to physical entanglement of the macroalga, increasing the likelihood that they can attach and so reducing the proportion lost, however this effect was not seen in this study since we used an excess seeding density, ten-fold higher than the number of fronds that developed. Experimental manipulation of this seeding density could be used to determine the optimal density and proportion washed away on different seeded materials. During the attachment period, when the binder is still present, it is highly likely that the prevailing weather conditions will strongly influence the sporophyte/gametophyte attachment success. Higher water motion due to storms will wash the binder solution away more quickly, while low light will limit growth and holdfast development. Further testing of the binder formulation dependent on the prevailing

5. Conclusions This study has demonstrated that the sporophyte seeding technique using a binder is an effective method to allow textile substrates to be seeded for macroalgal cultivation. Sporophyte seeding resulted in twice the final biomass yield compared with gametophyte seeding, due to a 2–3 week developmental lag, while meiospore seeding gave very poor results. The non-woven textile tested, had high initial fouling, but gave an equivalent final biomass to when Kuralon twine was either A) seeded with sporophytes or B) seeded and grown within a traditional hatchery. However, the method needs further optimisation and testing to ensure it is reliable. References [1] A. Handå, S. Forbord, X. Wang, O.J. Broch, S.W. Dahle, T.R. Størseth, K.I. Reitan, Y. Olsen, J. Skjermo, Seasonal- and depth-dependent growth of cultivated kelp (Saccharina latissima) in close proximity to salmon (Salmo salmar) aquaculture in Norway, Aquaculture 414-415 (2013) 191–201. [2] B.H. Buck, C.M. Buchholz, The offshore-ring: a new system design for the open ocean aquaculture of macroalgae, J. Appl. Phycol. 16 (2004) 355–368. [3] M.T. Burrows, Influences of wave fetch, tidal flow and ocean colour on subtidal rocky communities, Mar. Ecol. Prog. Ser. 445 (2012) 193–207. [4] D.A. Smale, M.T. Burrows, P. Moore, N. O'Connor, S.J. Hawkins, Threats and knowledge gaps for ecosystem services provided by kelp forests: a northeast Atlantic perspective, Ecol. Evol. 3 (2013) 4016–4038. [5] S. Forbord, J. Skjermo, J. Arff, A. Handå, K.I. Reitan, R. Bjerregaard, K. Lüning, Development of Saccharina latissima (Phaeophyceae) kelp hatcheries with yearround production of zoospores and juvenile sporophytes on culture ropes for kelp aquaculture, J. Appl. Phycol. 24 (2012) 393–399. [6] J.C. Sanderson, M.J. Dring, K. Davidson, M.S. Kelly, Culture, yield and bioremediation potential of Palmaria palmata (Linnaeus) Weber & Mohr and Saccharina latissima (Linnaeus) C.E. Lane, C. Mayes, Druehl & G.W. Saunders adjacent to fish farm cages in northwest Scotland, Aquaculture 354–355 (2012) 128–135. [7] G.S. Marinho, S.L. Holdt, M.J. Birkeland, I. Angelidaki, Commercial cultivation and bioremediation potential of sugar kelp, Saccharina latissima, in Danish waters, J. Appl. Phycol. 27 (2015) 1963–1973. [8] A.D. Hughes, K.D. Black, I. Campell, J.J. Heymans, K.K. Orr, M.S. Stanley, M.S. Kelly, Comments on ‘Prospects for the use of macroalgae for fuel in Ireland and UK: an overview of marine management issues’, Mar. Policy 38 (2013) 554–556. [9] C. Peteiro, N. Sánchez, C. Dueñas-Liaño, B. Martínez, Open-sea cultivation by transplanting young fronds of the kelp Saccharina latissima, J. Appl. Phycol. 26 (2014) 519–528. [10] M. Troell, D. Robertson-Andersson, R.J. Anderson, J.J. Bolton, G. Maneveldt, C. Halling, T. Probyn, Abalone farming in South Africa: an overview with perspectives on kelp resources, abalone feed, potential for on-farm seaweed production and socio-economic importance, Aquaculture 257 (2006) 266–281. [11] T. Chopin, S. Robinson, M. Sawhney, S. Bartarache, E. Belyea, R. Shea, W. Armstrong, I. Stewart, P. Fitzgerald, The AquaNet integrated multi-trophic aquaculture project: rationale of the project and development of kelp cultivation as the inorganic extractive component of the system, Bull. Aquac. Assoc. Can. 104 (2004) 11–18. [12] J.C. Sanderson, C.J. Cromey, M.J. Dring, M.S. Kelly, Distribution of nutrients for seaweed cultivation around salmon cages at farm sites in north–west Scotland, Aquaculture 278 (2008) 60–68. [13] S. Kraan, Mass-cultivation of carbohydrate rich macroalgae, a possible solution for sustainable biofuel production, Mitig. Adapt. Strateg. Glob. Chang. 18 (2013) 27–46. [14] A.D. Hughes, K.D. Black, I. Campbell, K. Davidson, M.S. Kelly, M.S. Stanley, Does seaweed offer a solution for bioenergy with biological carbon capture and storage? Greenhouse Gases Sci. Technol. 2 (2012) 402–407. [15] A.D. Hughes, M.S. Kelly, K.D. Black, M.S. Stanley, Biogas from macroalgae: is it time to revisit the idea? Biotechnol. Biofuels 5 (2012) 86–92. [16] D.R. Schiel, M.S. Foster, The population biology of large brown seaweeds: ecological consequences of multiphase life histories in dynamic coastal environments, Annu. Rev. Ecol. Syst. 37 (2006) 343–372. [17] P.D. Kerrison, M.S. Stanley, M. Kelly, A. Macleod, K.D. Black, A.D. Hughes, Optimising the settlement and hatchery culture of Saccharina latissima (Phaeophyta) by manipulation of growth medium and substrate surface condition, J. Appl. Phycol. 28 (2016) 1181–1191. [18] D.J. Tovey, B.L. Moss, Attachment of the haptera of Laminaria digitata (Huds.) Lamour, Phycologia 17 (1978) 17–22. [19] S.I. NV, Belgian patent application BE2013/0839, Filed 13/12/2013. [20] M. Edwards, L. Watson, F. O'Mahony, L. Connellan, M. Dring, A. Werner, Cultivating Laminaria digitata, Bord Iascaigh Mhara, Dun Laoaghaire, 2011. [21] M. Kawachi, M.-H. Noël, Sterilisation and sterile technique, in: R.A. Andersen (Ed.), Algal Culturing Techniques, Elsevier Academic Press, London, 2005, pp. 65–82. [22] T.W. Anderson, D.A. Darling, Asymptotic theory of certain “Goodness of Fit”

356

Algal Research 33 (2018) 352–357

P.D. Kerrison et al.

concentration, and temperature, Mar. Biol. 144 (2004) 61–70. [25] K. Flavin, N. Flavin, B. Flahive, Kelp farming manual, A Guide to the Processes, Techniques and Equipment for Farming Kelp in New England Waters, Ocean Approved, Portland, 2013, p. 123.

criteria based on stochastic processes, Ann. Math. Stat. 23 (1952) 193–212. [23] European_Commission, Innovative Textiles to Boost EU Seaweed Farming, European Commission, Brussels, BE, 2014. [24] H. Steen, R. Scrosati, Intraspecific competition in Fucus serratus and F. evanescens (Phaeophyceae: Fucales) germlings: effects of settlement density, nutrient

357