Evaluation of the Bioremediation Capability of the Seaweed Aquaculture in Korea

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Transcription:

SSIAS Evaluation of the Bioremediation Capability of the Seaweed Aquaculture in Korea Sustainable Seaweed Integrated Aquaculture System

Team Work, S.J. Ryu and Y.H. Kang J.A. Lee Dept. of Marine Science, Pusan National University School of Environmental Science and Engineering, Inje University T.-H. Seo and J.-A. Shin Division of Aquatic Science, Yosu National University C. Yarish Dept. of Ecology and Evolutionary Biology, University of Connecticut, Y.-F. Yang USA Institute of Hydrobiology, Jinan University, China

Bilateral Project China Bioremediation effects of cultivation of large-sized seaweeds in the eutrophic mariculture areas P.I. Dr. Yu-Feng Yang Korea The development of environmentally sound integrated polyculture system P.I.

Interactions between Aquaculture and Environment Modification to the environment Waste products - eutrophication Interactions with wildlife Use of resources Example Caged salmon farming Water movement and quality Sedimentation and benthic enrichment Introduction of exotic species

Priority Areas for Further Research (FAO) the adoption of aquaculture by poor rural households; technologies for sustainable stock enhancement, ranching programmes and open ocean aquaculture; the use of aquatic plants and animals for nutrient stripping; integrated systems to improve environmental performance; managing the health of aquatic animals; nutrition in aquaculture; the quality and safety of aquaculture products; emerging technologies, including recirculating systems, offshore cage culture, integrated water use, artificial upwelling and ecosystem food web management, domestication and selective breeding and genetic improvement.

Old Wisdom : Ultimate Solution Can seaweed aquaculture reduce the environmental impact of cultural eutrophication in the coastal environment? Can the integration of seaweed aquaculture with fed aquaculture be the solution of bioremediation of eutrophication caused by nutrient rich effluents from finfish and other forms of fed aquaculture in the coastal ecosystem? Why do we consider the Sustainable Seaweed Integrated Aquaculture System (SSIAS)?

Production Technology SUSTAINABILITY OF AN AQUACULTURE SYSTEM Asian Institute of Technology (1994) Productive SUSTAINABLE AQUACULTURE SYSTEM Socially relevant and profitable Social and Economic Aspects Environmentally compatible Environmental Aspects

Integrated Culture Examples Israel: Sea bream+ulva; abalone+fish+ulva; abalone+fish+ mollusc+ulva China: Shrimp+crab+seaweeds; mussel+scallop+ Laminaria/Undaria Japan: shrimp+ulva European estuary: integrated polyculture system Norway: salmon+mussel+seaweed Canada (northwest): salmon+porphyra Hawaii: shrimp+gracilaria Chile: seaweed biofilter - Gracilaria + salmon Philippine (with Norway): sea urchin/sea cucumber+ Eucheuma/Gracilaria France: sewage treatment system-ulva South Africa: finfish aquaculture effluent+gracilaria Southeast Asia: shrimp + seaweeds Australia: shrimp + oyster + Gracilaria, Saccostrea

Polyculture Experiences in Korea Studies on the development of polyculture system in the coastal waters of Korea Background Decreased aquaculture productivity Over-stocking, loss of culture grounds, increase in land-fills, pollution - i.e. cultural eutrophication, industrial contamination, etc. Sustainability Objectives To do feasibility study and analyses of polyculture To develop practical guidelines for polyculture National Fisheries Research Institute Period: 199-1994

Polyculture

Polyculture

Polyculture

Study Areas and Aqucultured Species Southeastern coastal area Sea squirts (Halocynthia roretzi) Seaweeds (Undaria pinnatifida, Laminaria japonica) Mid-western coastal area Abalone (Haliotis discus hannai) Seaweeds (Laminaria japonica, Hizikia fusiformis) Southwestern coastal area Short necked clams (Ruditapes philippinarum) Surf clams (Macta veneriformis) Seaweed (Porphyra tenera) Southern coastal area Oyster (Crassostrea gigas), sea squirts (Halocynthia roretzi), blue mussel (Mytilus edulis)

Aquaculture Production in Korea 8 5 4 4 Production (in 1 M/T) 6 4 2 seaweeds mollusca others crustacea fishes (fishes) 4 3 2 1 Fish Production (in 1 M/T) (in M / T) 3 2 1 Total production Culture Culture/Total (%) 3 2 1 (%) 196 197 198 199 2 YEAR 196 197 198 199 2 YEAR

Aquaculture of Fish Net cage Tanks or pond

SSIAS Project Overview Concept: Integrate and balance extractive and fed aquaculture Sustainability Fed and extractive culture system Seaweeds & shellfish Environmentally soundness Biofilter/production system : Seaweeds Socio-economically viability Species Temperature, light intensity, photoperiod, etc. Cultivars Wild species

First Step : Selection of Species Lab Experiments and Field Survey Cultivars and wild species Porphyra, Undaria, Laminaria, Enteromorpha etc. Field survey (all seasons) Ecophysiological studies (biofiltration capabilities) Physiology under high ammonia concentration Photosynthetic rates Nutrient (ammonium) uptake rates Growth rates Environmental factors Seed stock Simple uptake and growth model Simulation

Lab scale experiments Field Survey Short - term Long - term Pilot tank culture study

Field Survey Biomass (g fw m -2 ) 12 1 8 6 4 2 Green Red Brown Ammonia Nitrate Phosphate St. 1 12 1 8 6 4 2 Nitrate & Ammonium (µm) 4 3 2 1 Phosphate (µm) 14 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec St. 2 3 1. Biomass (g fw m -2 ) 12 1 8 6 4 2 25 2 15 1 5 Nitrate & Ammonium (µm).8.6.4.2 Phosphate (µm) 3 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec St. 3 14. 1.2 Biomass (g fw m -2 ) 25 2 15 1 5 12 1 8 6 4 2 Nitrate & Ammonium (µm) 1..8.6.4.2 Phosphate (µm) Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec 22.

7 Seaweed tissue nitroten content and seawater nutrient (Tongyong) 6 4 Field Survey Tissue N content (%) 6 5 4 3 2 N (%) Ammonia Nitrate Phosphate St. 1 5 4 3 2 Nitrate & Ammonia (µm) 3 2 1 Phosphate (µm) 1 1 7 6 4 6 St. 2 5 Tissue N content (%) 5 4 3 2 4 3 2 Nitrate & Ammonia (µm) 3 2 1 Phosphate (µm) 1 1 7 3 4 6 St. 3 25 Tissue N content (%) 5 4 3 2 2 15 1 Nitrate & Ammonia (µm) 3 2 1 Phosphate (µm) 1 5 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Jan Feb Mar Apr 22 23

7 Field Survey Tissue Nitrogen (%) 6 5 4 3 2 1 1 2 3 4 5 6 22 2 18 Nitrate (µm) Tissue C/N ratio 16 14 12 1 8 6 4 2 1 2 3 4 5 6 Tissue Nitrogen (%)

Rates of ammonium uptake Porphyra yezoensis Enteromorpha sp. NH + Uptake rate 4 NH + (μmol g (μm) dw min - 4 Uptake rate 1 (μm) (μmol g ) dw min -1 ) v -2 4.16±.117 4.394±.44 75.245±.31 75.57±.13 15.885±.187 15 1.673±.115 25 1.449±.8 v 6-12 4.15±.81 4.116±.79 75.211±.77 75.57±.5 15.56±.198 15.125±.66 25.775±.173 Laminaria japonica (tank) V -.5 1.776-2.52 V 2-11.86.9

Second Step: Mid-Sized Pilot System Scaled-up system Large tank systems (>4m 3 ) Population level parameters Biofilter Growth, production and harvesting Physical set-ups Closed, flow-through Flushing rate, flow rate, mixing (aeration) Stocking density Simple model for biofilter/production efficiency Nutrient cycle and budget (nitrogen, phosphorus) Nutrient removal efficiency

Pilot Tank Culture Study (Finfish Seaweed) Acanthopagrus schlegeli (Bleeker) Ulva pertusa Kjellmann

45 4 35 NH 4 + (µm) 3 25 2 15 1 1 2 3 4 5 Time (hr)

5 45 4 Fish tank Seaweed tank (Difference) 14 12 1 NH 4 + (µm) 35 3 25 8 6 4 NH4 + (µm) 2 2 15 1 1 2 3 4 5 Time (hr)

14 1 12 8 1 6 NH 4 + (µm) 8 6 4 2 NH4 + (µm) 4 2 Fish tank Seaweed tank (Difference) 1 2 3 4 5 Time (hr) -2-4

flow rate fish tank NH3 conc flow rate ~ fish tank seaweed tank excretion effluent uptake recirculation recirculation flow rate ~ seaweed tank NH3 conc

feeding rate food conversion rate fish biomass Excretion flow rate fish tank NH3 conc flow rate ~ fish tank seaweed tank excretion effluent uptake recirculation recirculation flow rate ~ seaweed tank NH3 conc Uptake seaweed biomass uptake rate growth harvest growth rate Uptake

Final step: Field application and operation Earthen ponds, tanks and raceways with aeration and ph controls Floating net cage with long-lines and rafts Ecosystem and carrying capacity models Odum (1993) Inputs from outside the system; Processing functions; Outputs to the external environment Rawson et al. (22) Understanding the carrying capacity of coastal waters for aquaculture 3-D physical, chemical, and biological simulation Jailhouse Bay and Incan Bay (Sino-US Living Marine Resources Panel) Ilk Kayo Chung

Conclusion The amount of nitrogen removed by seaweeds aquaculture should not be underestimated The best practices for the SSIAS should be applied immediately.

SSIAS Thank you

Shellfish Production 12 1 8 6 4 2 Year Monthly Production (1 3 ton) 5 Annual Production (1 3 ton) 4 3 2 1 1991 19921993 1988 1989199 1994 19951996 2 2122 1997 19981999

Seaweeds Production 3 25 2 15 1 5 Monthly Production (1 3 ton) 1989 1988 1991 199 1993 1992 1995 1994 1997 1996 1999 1998 21 2 8 Annual Production (1 3 ton) 6 4 2 22

5 4 3 2 1 Year Monthly Production (1 3 ton) Annual Production (1 3 ton) Finfish Production 7 6 5 4 3 2 1 1991 19921993 1988 1989199 1994 19951996 2 2122 1997 19981999

Crustacean Production 12 1 8 6 4 Year Monthly Production (ton) Annual Production (ton) 25 16 14 2 15 1 5 2 1991 19921993 1988 1989199 1994 19951996 2 2122 1997 19981999