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  • Experiments on cultivation of economically important seaweeds such as Gracilaria edulis, Gelidiella acerosa, Sargassum spp and Turbinaria spp have been carried out during the past few years at the Central Marine Fisheries Research Institute. A suitable technique of culture of the agarophyte Gracilaria edulis has been developed. Technique for culturing the other seaweeds have not yet been streamlined. The culture technology developed for G. edulis comprises of introduction of small fragments of the seaweed into the twists of the coir rope fabricated in the form of nets and tied to the fixed poles in the inshore waters and monitoring their growth.

    Author(s): Chennubhotla, V S Krishnamurthy, Kalimuthu, S, Ramalingam, J R, Najmuddin, M, Kaliaperumal, N
  • Low-input high-diversity (LIHD) mixtures of native grassland perennials were subjected to a supercritical treatment process with the aim of obtaining hydrogen-rich gases. The process was studied based on the following treatment variables: reaction temperature (374 degrees C to 575 degrees C, corresponding to a pressure range of 22.1 to 40 MPa), residence time (10 to 30 min), biomass content in the feed, and catalysts (0% to 4% NaOH and solid alkali CaO-ZrO(2)). The gaseous phase produced from gasification of LIHD primarily consisted of hydrogen (H(2)), with a mixture of carbon monoxide (CO), methane (CH(4)), and carbon dioxide (CO(2)). The statistical significance of treatment variables was evaluated using analysis of variance (ANOVA). It showed that at the level of P < 0.05, temperature, catalysts, and biomass content in the feed significantly affected gas yields, while residence time was not significant.

    Author(s): Kenneth Valentas, Marc von Keitz, Zhigang Zhang, Bo Zhang
  • Methane is the second most important greenhouse gas emitted from anthropogenic activities with a global warming potential 23 to 25 times higher than that of carbon dioxide. The agricultural sector is a major contributor to methane emissions with ruminant livestock production as the main source within the sector. Ruminant emissions account for 7 to 18% of total global greenhouse gas emissions. Due to the impact that methane has on the climate, several approaches have been developed to mitigate the emission of methane from ruminants. Among these approaches, nutritional strategies are the most developed and likely to be implemented at farm scale because they have the potential to reduce enteric methanogenesis and increase animal performance and overall production. This thesis investigated the potential of tropical macroalgae as a natural alternative for the mitigation of greenhouse gas emissions, particularly CH₄, for the beef industry. In a first experiment the antimethanogenic activity and nutritional value of twenty species of tropical macroalgae were evaluated in vitro (Chapter 2), at an inclusion rate of 16.7% of the total organic matter using rumen fluid from Bos indicus steers fed a low quality roughage diet characteristic of northern Australia. All species of macroalgae resulted in lower total gas and methane production than decorticated cottonseed meal (CSM). The freshwater macroalga Oedogonium, demonstrated a rich nutritional profile which resulted in a decrease in the production of methane of 30.3%, however, increased the production of total volatile fatty acids (VFA) by 20% compared to CSM control. In contrast, Asparagopsis had the strongest effect inhibiting methanogenesis by 98.9% compared to CSM. However, this species also had the lowest concentration of VFA, indicating that anaerobic fermentation was also affected. In a second experiment, the potential to maximize the mitigation of the production of methane while minimizing the effects on in vitro fermentation was investigated (Chapter 3). This experiment demonstrated that Asparagopsis was highly effective in inhibiting methanogenesis with a reduction of 99% at doses as low as 2% organic matter (OM) basis. At this dose, the negative effects of Asparagopsis were minimized, with no significant effects on degradability of organic matter and pH. In addition, combining Asparagopsis (2% OM) and Oedogonium (25 and 50% OM), demonstrated that the antimethanogenic activity of Asparagopsis was not affected by the nutritional value of the basal substrate. The effectiveness of Asparagopsis demonstrates its potential for the mitigation of methane emissions from ruminants at inclusion rates of ≤2% OM. In a third experiment, the secondary metabolites responsible for the antimethanogenic activity of Asparagopsis were elucidated (Chapter 4). This experiment identified bromoform as the most abundant secondary metabolite within Asparagopsis biomass. Bromoform was the only metabolite present in sufficient quantities in the biomass (≥1 μM) to drive the antimethanogenic activity of Asparagopsis. Notably, at this concentration the fermentation parameters of degradability of organic matter and total volatile fatty acids were not adversely affected. In a fourth and final experiment, the mode of action of Asparagopsis and bromoform was elucidated at the microbial level (Chapter 5). Quantitative PCR demonstrated that the decrease in the production of methane induced by Asparagopsis and bromoform was directly correlated with a decrease in the relative number of methanogens. High throughput amplicon sequencing confirmed that both treatments decreased the overall number of OTU sequence reads of the three dominant orders of methanogens Methanobacteriales, Methanomassiliicoccales and Methanomicrobiales. Asparagopsis and bromoform also led to an increase in the accumulation of hydrogen within the gas phase, which was reflected in a decrease of the number of sequence reads of hydrogenproducers and an increase in the number of sequence reads of hydrogen-consumers and species that are less sensitive to the increase of the partial pressure of hydrogen. Nevertheless, the minimal effects on microbial fermentation shown in previous chapters supports that the rumen microbial ecosystem is robust, with the decrease in abundance of some species being compensated functionally by the proliferation of others. Therefore, the outcomes of this thesis consistently demonstrate that Asparagopsis is a promising and potent natural alternative to other antimethanogenic agents for mitigation of enteric CH₄ emission through the direct inhibition of populations of enteric methanogenesis.

    Author(s): Lorenna Machado
  • Several.concepts have been developed for tropical marine biomass cultivation for bioconversion to methane. These concepts take advantage of Florida's large areas of relatively shallow water. One concept, tidal flat seaweed farms, uses currently available macroalgal candidates (Gracilaria, Ulva) and at biomass yields of 12-25 dry ash free tons/hectare-year can-provide delivered low feedstock costs of · $40-25/DAFT, or on an energy basis, $3.60-2.30/G joule, respectively. These biomass yields are close to those achieved in commercial Gracilaria culture in Taiwan. Such systems would be constrained to nearshore waters of 0.5-1.5 m in depth, of which there are 190,000 hectares in northwestern Florida.

    Concepts which would work in deeper waters (from 1.5-20 m depths) use floating seaweeds. Such biomass species would need to be produced by genetic breeding and hybridization, as there is not an adequate natural species available which also has high bioconversion rates. Such hybrids may be intrageneric ones of Sargassum, or Sargassum hybrids with other algae such as Macrocystis. A biotechnology approach could provide competitive feedstock costs with a large potential gas production, as there is approximately 1,900,000 hectares between 1.5-20 m depths in northwestern Florida.  

    Author(s): Kimon T. Bird
  • Executive Summary

    Performance assessment, regional tuning and validation of a software program known as AquaModel were the primary goals of this study. The software was designed for use by governments and industry to predict the sea bottom and water column effects of fish aquaculture. From an industry perspective, it also includes advanced tools to optimize fish production by obviating the usual trial and error method of configuring pen spacing and loading, by estimating optimum fish loading and culture density for growth in relation to currents and ambient oxygen supply.

    The benthic submodel of AquaModel software was applied, tuned and validated at the Blue Ocean Mariculture LLC fish farm site near Kona on the big island of Hawai’i (herein “study site”). Fish production is relatively small at present and this factor, combined with the deep water location and moderately strong current velocity and variable directions of flow allows the organic wastes from the farm to be spread over a very large area and readily assimilated into the food web without perturbations. Seven years of field data from five locations was collected by an independent scientist who reports to the State of Hawaii government for this study. To more accurately simulate the fish farm waste production, AquaModel staff created the first physiological and growth model of the cultured fish, Seriola rivoliana (aka KampachiTM or Almaco jack) and tuned this submodel to produce the same growth patterns and food conversion ratios seen at the study site.

    Model Overview

    AquaModel is composed of interlinked submodels of fish physiology, hydrodynamics, water/sediment quality, solids dispersion and assimilation into the aquatic food web. The model simultaneously calculates and displays a time series of water and sediment quality conditions resulting from fish feed ingestion, fish growth, respiration, excretion, and egestion. The user is presented with a 3-dimensional video-like simulation of growth, metabolic activity of caged fish, associated flow and transformation of nutrients, oxygen, and particulate wastes in adjacent waters and sediments. The software is used by government managers and researchers in several locations worldwide and is presently being formally validated in Canada and Chile at five large fish farms. These validation activities have necessitated numerous upgrades and new utilities in AquaModel, some that are described herein.

    New Fish Submodel

    Solid wastes dynamics in the model are calculated from feed consumed and a small percent of waste, as well as the assimilation efficiency and food conversion ratio. These results were compared to measurements and estimates from the fish farmers as a quality assurance measure. A physiological model of the cultured fish species reared at Blue Ocean Mariculture (Seriola rivoliani, aka “KampachiTM”) was created for this project and tested to produce growth and food conversion efficiency results similar to that achieved at the farm site.

    Circulation of Study Site and Prior Monitoring Results

    Accuracy of aquaculture models is strongly related to the quality of the physical oceanographic inputs, particularly in open ocean conditions where non-tidal forcing factors result in considerable variation of flow rates and directions. Two months of continuous surface to bottom (ADCP) current meter records were collected every 20 minutes at the center of the net pen area lease. Surface currents above submerged net pen depth were strong, averaging about 28 cm s-1, but these subsurface readings were affected to some degree by backscatter from the water-air interface. Reliable current velocity readings were obtained from about 10 meters depth (top of submerged net-pen depth and below) to a few meters above the bottom averaging about 9 to 13 cm s-1 (SD range 7 – 9 cm s-1). Polar current vector diagrams produced by AquaModel indicated good dispersion flows in all directions with dominance to the northeast and southwest at net-pen depth and flowing mainly to north and south nearest the sea bottom. These characteristics indicate suitable conditions for rearing fish and provide regular resuspension of solid wastes on the sea bottom. Resuspension allows for aerobic assimilation of the waste feed and fish feces.

    The sea bottom was composed of a thin, coarse-sand layer over hardpan and had very low background (reference station) total organic carbon concentrations (TOC) of about 0.14% (SD = 0.03) as measured over several years of monitoring. There were four reference areas sampled and one near-net-pen location from the center of the aquatic lease area. Field data suggested only a possible increase of about 0.1 to 0.2 %TOC near the center of the net pen locations to values of 0.15 or 0.16 %TOC (SD = 0.05), respectively. Statistical difference (p =0.035, df =6) was found comparing sediment TOC results of annual mean from a reference area to the center of the net pen area. No field data were available from sediments immediately adjacent to the net pens but the model produced estimates for all locations.

    Modeling Challenge

    Because of the naturally low organic carbon content of the sea bottom and the relatively small size of the fish farm and the limitations of a single net pen area sampling location, it was not certain at the outset that the model could produce reasonable results. Typically, aquaculture models are used at or for planning of fish farms that may be much larger than the Blue Ocean Mariculture project. Most other farms are located in shallower water, sometimes with lesser current velocity and this produces a strong benthic-effects signal. Therefore, the signal to noise ratio is high for these other farms, but low by a factor of about 5 to 10 or more for the study site. The model was set up to grow concurrent crops of KampachiTM in each cage to a total fish biomass of 590 metric tons, slightly exceeding previous annual production. Figure 1 illustrates one of thousands of frames of the video-like output that the model produces. This one is from near the end of the fish production simulation with maximum fish biomass. The color scale in Figure 1 was adjusted to show an extremely low range of TOC concentrations. Solid green color indicates values of about 0.18 %TOC or about 0.04 %TOC above background, a difference that is similar to the normal error range of a high-precision laboratory analysis.

    Model Performance

    After calibrating and tuning the AquaModel to regional conditions, it produced background (reference) conditions within >0.001 %TOC of measured, steady-state reference-station values. This is essentially no difference between modeled and measured and certainly not with respect to measurable outcomes in the field. This is noteworthy as other benthic aquaculture models have been unable to maintain background organic carbon steady state concentrations due to resuspension washing TOC out of their modeling domains. With AquaModel, best estimates of the results at the single sampling station nearest the net pens were within<0.0012 %TOC of measured, long-term average results for the best-tuned setup. AquaModel consistently produced slightly higher sediment TOC concentration estimates (<0.02% TOC) at other locations nearer the two largest pens that had no corresponding field data measurements to verify the model predictions at these locations. All of the >250 simulations performed for this study indicated the same spatial pattern of increased TOC, with differing values depending on the calibration settings. None of the TOC concentrations measured or modeled indicated any risk of sea bottom eutrophication or probable significant biological change.

    Validation Outcome

    This study indicates that the tuned and validated AquaModel program should be sufficiently robust to model other open ocean locations of the leeward shores of the Hawai’ian Islands. The model is designed to work effectively with much higher levels of sediment organic carbon loading from fish farms, but not at grossly eutrophic cage sites in some sheltered, inshore cage locations utilized decades ago. AquaModel use would readily identify such outcomes through observation of several parameters, such as TOC delivery rate to the bottom (“TOC Rate”, in grams carbon per m2 per day) as well as sediment interstitial oxygen and sediment sulfides results. With separate cages that are spaced appropriately, most open ocean locations on the leeward shores of the Hawai’ian Islands that are in sufficient depth of water would not produce eutrophic or even modestly elevated sediment conditions. However, some habitats are considered of special biological significance, where net pen siting should not be considered.

    Overview and AquaModel Use in Hawai’i

    This evaluation, along with the existing routine monitoring program at the subject site as well as other analyses cited herein, indicate that the fish farm operation is not adversely affecting benthic conditions in the area. The waste tracking utilities of AquaModel applied to this particular site indicate that a small fraction of the waste fish feces reaches locations outside the modeling domain. The estimated loading rate of organic carbon in those locations are so minimal at present that it produces no measurable or even modeling-predicted change in concentration of sediment TOC. The chance of changing the biology of the benthos at these same locations is therefore highly unlikely. In general, small amounts of TOC added to the sea bottom from any source in the marine environment have been found to increase biodiversity and abundance of benthic organisms, but often at nearshore fish farms, these levels are exceeded. AquaModel provides a convenient and relatively accurate means of estimating future carrying capacity for this farm or groups of farms in the future. It also should be used to inform future monitoring efforts, rather than selecting sampling locations through best guess or randomly. Now that regional tuning is complete, configuring and running the model is not difficult for other locations similar to the west coast of the Big Island of Hawai’i and in other similar habitats throughout the region.

    AquaModel validation continues at other sites around the world that are larger in fish biomass and more replete with measurement locations in the field. Optimum model calibrations or trends identified in this study were in many cases as expected and occurred in other model validation locations. These findings, combined with prior model use experience and published literature guidance gives us confidence that the validation procedure employed herein is not a product of simple coincidence.

    Author(s): J.E. Rensel, F.J. O’Brien, Z. Siegrist, D.A. Kiefer
  • Seaplants such as macroalgae, microalgae, sea-grasses and mangroves form the primary productivity base for seashore habitats and integrated multi-trophic aquaculture (IMTA) systems. The foundation for sustainable seashore development is therefore the effective utilization, cultivation and management of seaplant populations.

    In the long run the aquaculture productivity of global seashores can be maximized if seaplants are effectively developed as cash crops, feeds, fodder and bio-mitigation agents within IMTA systems that make optimal use of lower trophic-level species.

    In the Coral Triangle 400 million people live in archipelagos that have 100,000 kilometres of tropical seashore distributed among more than 25,000 islands. About 80 million of these people live below the poverty line and many aspire to gain a sustainable livelihood from well managed seashore habitats.

    IMTA development along Coral Triangle seashores can generate tens of billions of USD in annual income for micro, small and medium enterprises owned and operated by the coastal people of the Coral Triangle. IMTA can be developed on the basis of already existing technology, it addresses existing market demands, it can alleviate poverty for millions of people and it can generate positive environmental impacts. Stimulating adequate investment in this opportunity will generate substantial benefits that can be realised in the coming
    decades.

    Author(s): Iain C. Neish
  • As a response to growing land and freshwater shortages and climate change, the use of seaweeds as food, their cultivation at sea and its effect on biodiversity are being researched on both the Caribbean and Pacific coasts of Costa Rica. Native species, more plentiful on the Caribbean coast, were collected and pre-selected based on existing information and on criteria including ubiquity, abundance, growth and palatability. These species were then evaluated as food and subjected to floating long-line cultivation using vegetative propagules. After establishing postharvest procedures, use as food involvedmany preparations to be eaten fresh or after drying, including a dry-ground meal. Ten of these species, which had nutrient contents within expected values including 9.8% crude protein on a dry weight (dw) basis and high iron, were considered adequate as food, both directly and as part of recipes in quantities not exceeding 20% dw of a given dish. Higher concentrations either ‘overwhelmed’ traditional recipes or their taste was rejected by tested consumers. Near-coast cultivation was in general a simple matter, easily transferred to artisanal fishers. To a great extent due to herbivory and theft of ropes, yield (ranging from 51.7 to 153.2 t ha−1 yr−1 on a fresh weight basis) was quantified for only five species with amean of 9.3 t ha−1 yr−1 dw, equivalent to 0.91 t ha−1 yr−1 of crude protein—very similar to yields of two grain crops per year. Species of Codium, Gracilaria, Sargassum and Ulva were considered adequate both for use as food and cultivation. Cultivated seaweed plots rapidly attracted biodiversity, including a significantly larger number of fish species and individuals than nearby control areas. Based on this we postulate the need to further explore a ‘biodiversity enrichment’ service from seaweed cultivation and any effect of this on fisheries enhancement. While noting areas in which further research and international collaboration are needed, it is concluded that tropical seaweeds, besides their many other uses, can at this stage substitute up to 15% of food on a dry weight basis, their cultivation is simple, and effects on biodiversity are a previously undocumented advantage. Given the lack of experience in most of the world excepting some Asian countries, the agriculture-like approach followed here may be of use to others in tropical developing countries who wish to explore seaweed cultivation at sea, for food and other products and for environmental/biodiversity services.

    Author(s): Ricardo Radulovich, Schery Umanzor, Rubén Cabrera, Rebeca Mata
  • IB is defined as “the use of biological substances* for the processing and production of enzymes, chemicals, materials and energy”.

    *plants, algae, marine life, fungi, micro-organisms

    The estimated global market for IB by 2025: £150 bn - £360 bn

    Whilst for the UK: £4 bn - £12 bn

    Across a range of sectors: personal care, pharma, food/drink, biofuels & other chemical sectors.

    IB can play a critical role in maintaining UK competitiveness in global markets and in the creation of a low-carbon knowledge-based economy in the UK.

    Author(s): Michelle Carter
  • The Mexican tunafleet catches mainly yellowfin tuna and, to a lesser extent, skipjack tuna in thewarm waters of the eastern Pacific Ocean.These catches are primarily for canning. Ensenada usedto be the main tunafishery port in Mexico, and almost all of its production was exported to theUnited States.

    A few years ago, thefleet moved to the southern ports of Mazatlan and Manzanillo, located closer tothefishing grounds and the major national markets, mainly Mexico City, Guadalajara and Monterrey.Thisfleet relocation negatively impacted the port of Ensenada, but bluefin tuna farming has beenestablished nearby as a lucrative added-value activity off the coast of Baja California. Wild tuna arecaught and stocked intofloating pens, where they are fed until they gain enough weight and fat tomeet market demands.

    Author(s): Yarish, Charles Jose A. Zertuche-Gonzalez, Barry A. Costa-Pierce, Juan Guillermo Vaca-Rodriguez, Raul del Moral Simanek, Oscar Sosa-Nishizaki
  • "With Earth's burgeoning population to feed we must turn to the sea with new understanding and new technology. We must farm it as we farm the land" - Jacques Cousteau 1973

    Cousteau didn't explain what he meant by this. I'll try and explain today whait it means to me. 

    Author(s): Forster, John

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