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Greenhouse-Enclosed
Raceway System at Waddell
Mariculture Center
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Introduction
Several
factors have limited the growth
and expansion of the pond-based
shrimp farming industry in the
United States (US). Extensive
and semi-intensive pond production
systems are typically managed with
high rates of water exchange (Boyd
and Clay 1998). This production method raises environmental
concerns regarding effluent discharge
into receiving waters (Hopkins
et al. 1995; Goldburg and Triplett
1997; Boyd and Clay 2002). Pond-based culture systems are also typically restricted to coastal
regions, where land costs are inherently
high (Landesman 1994). Another major concern is the limited growing
season often found in temperate
and subtropical regions. For example, in coastal South Carolina water
temperatures conducive for shrimp
production only exist six to seven
months per year. This
factor restricts overall production
and usually allows only one crop
per year (Main and Fulks 1990). Finally
several viral disease outbreaks
have caused major damage to pond
reared shrimp in the US and globally
(Brock et al. 1997; Flegel et al.
1997; Lightner et al. 1998; Lightner
1999).
In
response, some recent research
efforts in the US have
been focusing on the use of greenhouse
enclosed raceways for intensive
to super-intensive shrimp production
(Davis and Arnold 1998; Browdy
et al. 2001; Van Wyk 1999, 2000,
2001; Samocha et al. 2002). These production systems offer several advantages over the typical
pond-based systems. The
raceways can be managed with zero
to minimal water exchange thus
greatly reducing the environmental
impact due to effluent discharge
(Browdy et al.2001). Biosecurity
protocols can be implemented to
manage disease vectors (Moss et
al. 1998; Ogle and Lotz 1998; Bratvold
and Browdy 1999; Leung and Moss
1999; Moss 1999; Lotz and Lightner
2000). Greenhouse enclosed systems also provide opportunities
for inland culture operations (Scarpa
1998; Main and Van Wyk 1999) and
year round production can be achieved
(Browdy et al. 2001).
At
the Waddell Mariculture Center
(WMC) experiments have been carried
out on the application of greenhouse
enclosed super-intensive raceways
for nursery and growout culture
of Litopenaeus
vannamei. This article will
provide a brief description of
the systems, operational procedures,
and present some of the production
data.
System Description and Operational
Procedures
To
date, several juvenile and growout
production trials have been conducted
using pilot and commercial-scale
greenhouse-enclosed super-intensive
raceway systems. The
pilot scale system consists of
two 55 m2 HDPE-lined,
sediment-free raceways; the commercial-scale
system consists of a single 282
m2 unit. Each can be equipped with AquaMats™ for vertical
surface enhancement at a density
of about 1 m2 of mat
for each m3 of
raceway volume. Aeration and water movement has been supplied by blown air, and 0.75-kw paddlewheel and propeller-aspirator
units. Propane-based water heating is achieved using heat exchange
units in-situ (pilot-scale system)
or externally with a recirculating
water pump system (commercial-scale
system), which also aids in water
movement. Temperature is moderated
during warmer months via shade
cloth covering and thermostat-controlled
fans. Through
2002, no external biological or
mechanical filtration has been
employed during the production
trials. However,
during the last growout trial in
the 282 m2 commercial-scale
system, a 25 m3 bead
filter was operated during the
latter half of the cycle. Also in place of the paddlewheel and aspirator
units used in previous trials,
oxygen supplementation was provided
via injection by a Air Products
Specialty VSA oxygen generator
(Model No. A-150 L). Two
weeks prior to stocking of PL-10/20,
raceway units are filled with UV-sterilized
water and fertilized to establish
planktonic communities. For
juvenile production trials, PL
are stocked and then reared using
standard feeding and husbandry
protocols for 25-100 d. For
the most recent growout production
trials, juvenile animals (1g) were
stocked at 300 m2 and
then reared for 75-90d.
Results and Discussion
Nursery
Results obtained thus far confirm the technical feasibility
of the application of these technologies
for the nursery production of juvenile L.
vannamei. Results are shown
in Table 1. Survival
of animals produced in each trial
has been > 90%, with mean
Table 1. At-harvest
results of greenhouse-based trials
for the production of juvenile Litopenaeus
vannamei.
|
Time
of Stocking
|
Stocking
Density
|
Total
Days in Raceway
|
Survival(%)
|
Mean
Weight(g)
|
|
April/2001
|
1,950 PL/m²
|
97
|
98
|
1.01
|
|
April/2002
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1,950 PL/m²
|
28
|
97
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0.55
|
|
June/2002
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1,240 PL/m²
|
38
|
97
|
0.31
|
|
April/2002†
|
1,945
PL/m²
|
74
|
>90*
|
1.00
|
|
October/2002†
|
1,364 PL/m²
|
80
|
98
|
0.90
|
harvest
weight exceeding 0.25 g at 30 d
post-stocking. As
densities are increased, risks
associated with mechanical failure
increase. This necessitates investment in personnel,
emergency backup and alarm systems
to manage the additional risk of
catastrophic crop loss. In a recent
review, Samocha et al (2002) summarized
similar results from a range of
commercial and experimental scale
super-intensive nursery systems. Clearly,
the technologies for the large
scale biosecure super-intensive
nursery culture of L.
vannamei have matured such
that commercial implementation
can be quickly implemented with
a minimum of risk. Transfer of
juveniles to growout systems can
be quickly and efficiently carried
out. Transfer
mortality is minimal particularly
if oxygen is applied during the
transfer process. The
degree of intensification of the
nursery can be balanced with factors
such as target growth rate and
harvest size, capital investments
and application of water treatment
and oxygen injection technologies. The
advantages of the use of biosecure
super-intensive nursery systems
vary according to the site and
type of growout operation. In
more temperate zones and in areas
where shrimp growth improves seasonally,
these systems allow the grower
to gain three to four weeks of
growing time by stocking 1g juveniles
into the ponds at the start of
the optimal growing season. Typically
PL availability is limited during
optimal stocking windows and the
use of the nursery system to “head
start” and/or stockpile PL can
improve the outlook for stock availability
during optimal stocking windows
(Rhodes et al. 1995). For operations
in which culture can be carried
out year round, the use of the
head start system greatly increases
farm productivity allowing much
more efficient use of space and
increasing the number of cycles
which can be produced per year
and thus overall returns per unit
area. Holding of stock in raceways
for up to 30 days provides a powerful
quarantine option to assure stock
health before stocking into the
farm. This requires proper nursery
system site selection, planning
and design along with an effective
health monitoring protocols but
it can be one of the most important
components in an overall disease
risk management and farm biosecurity
program. Survival of nursed animals
in growout is typically much higher
and more predictable when compared
to direct stocked PL. This
allows for more efficient feed
management and can be an important
factor in overall farm profitability.
In areas where viral pathogens
are endemic, use of nursed juveniles
can improve survival rates by allowing
the animals to grow larger and
by improving the condition of the
shrimp before exposure to endemic
pathogens.
Growout
A
total of five growout production
trials were completed through 2002
in the Waddell Mariculture Center
super-intensive production systems
and were summarized by Weirich
et al. (2002). The trials demonstrated
the biological feasibility of the
systems while documenting several
bottlenecks which must be overcome
for successful commercialization. While
market size shrimp were produced
using minimal exchange systems
without external filtration, survival
and yield have been inconsistent.
The most important factor in maintaining
crop health and growth is adequate
supplemental aeration in the system.
In some trials, technical difficulties
with liner designs or power failures
in the absence of proper alarm
and backup systems caused catastrophic
failures. Clearly, one of the most
important guiding principles for
the design and implementation of
commercial scale systems must be
risk management through appropriate
engineering technologies and management
systems. By
designing in computer control systems
and adequate redundancy, crop loss
due to aeration failure should
be eliminated.
Table
2 shows production results for
trials 2 and 5. Both trials were
stocked at 200/m2 as PL8-10 for a 20 week growout cycle. Trends towards increasing production levels
and reduced feed conversion ratios
reflect improvements through experience
gained in completion of initial
trials. The results obtained suggest
that the system can operate without
any outside filtration or water
exchange up to a carrying capacity
of 3kg/m2.
Table
2. Harvest results of greenhouse-based
trials for
the production of Litopenaeus vannamei.
|
|
Trial
2: July-November 2000
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Trial 5:
December 2001-April 2002
|
|
|
RW
1
|
RW
2
|
RW 1
|
RW 2
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RW 3
|
|
Weight (g)
|
19.3
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18.9
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14.6
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15.4
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17.1
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|
Survival (%)
|
60.1
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63.9
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70.5
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71.5
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55.2
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FCR
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2.8
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2.8
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1.8
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2.0
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1.9
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Yield (kg/m2)>
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2.3
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2.4
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3.1
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3.3
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2.8
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Water
quality parameters from trial 5
are shown in Table 3. Temperature
was maintained at a stable optimal
levels by the heat exchange system
despite outside temperatures which
neared freezing on several occasions. Data on temperature inside and outside the
greenhouse and in the raceway coupled
with information on propane usage
will form the basis for system
engineering to optimize passive
heat gain and to provide a basis
for system financial feasibility
analyses for varying geographical
locations. In
trial 2 and in raceway 2 in trial
5, water from the previous run
was stored at harvest and reused
for the subsequent cycle. The
reuse of water coupled with a relatively
fast turn around and re-flooding
around the Aquamat material resulted
in consistently low ammonia and
nitrite levels. In
contrast, freshly filled and bloomed
tanks or use of new Aquamat material
resulted in midseason ammonia increases
followed by nitrite spikes. Thus,
system designs which reuse water
between crops may serve to stabilize
microbial communities and associated
water quality parameters while
enhancing opportunities for application
of these technologies away from
the coastal zone.
Table 3. Water
quality parameters recorded during Litopenaeus vannamei superintensive raceway production trial 5, December 2001-April
2003.
| |
RW 1 |
RW2 |
RW3 |
| |
New Water |
Old Water |
Pond Water |
| Temperature AM |
28.5 (25.7-30.3) |
29.5 (26.2-31.1) |
28.8 (25.7-30.5) |
| PM |
29.8 (25.9-31.1) |
28.5 (24.2-30.6) |
29.7 (25.0-32.7) |
| Dissolved Oxygen (mg/L) |
6.3 (5.0-7.9) |
6.1 (4.9-7.7) |
5.8 (4.3-7.2) |
| Salinity (g/L) |
15.0 (14.3-15.6) |
14.9 (14.1-16.1) |
15.1 (14.6-15.7) |
| pH |
7.7 (7.1-8.3) |
7.7 (7.1-8.2) |
7.6 (7.1-8.3) |
| Alkalinity (mg/L as CaCO3) |
180 (140-240) |
229 (160-340) |
144 (120-220) |
| Total Ammonia-Nitrogen (mg/L) |
0.01 (0-0.10) |
0.01 (0-0.10) |
0.15 (0-1.80) |
| Nitrite-Nitrogen (mg/L) |
0.13 (0.03-1.40) |
0.18 (0.03-0.50) |
0.94 (0-7.60) |
| Nitrate-Nitrogen (mg/L) |
22 (1-38) |
29 (10-40) |
19 (1-40) |
Results
from the most recent growout trial
continued to demonstrate trends
towards improvement in production
parameters (Table 4). At harvest
production results were:survival,
91%; mean weight, 16.6 g; FCR,
1.54; avg. growth/week, 1.44 g;
and yield, 4.50 kg/m² 10.0pt'.
For this trial the raceway was
stocked with 1g juveniles from
a nursery system. Together
with improved growth rates, growout
time was reduced to 11 weeks. Use of juveniles may also have contributed to the improvement in
survival rates.
Table 4. At-harvest results
of greenhouse-based trials for the production of Litopenaeus vannamei (March 2003).
|
Weight at stocking (g)
|
1.0
|
|
Final Weight (g)
|
16.6
|
|
Total Days Growout
|
76
|
|
Avg. Growth/day (g)
|
0.21
|
|
Avg. Growth/week (g)
|
1.44
|
|
Total Biomass Harvested (lbs)
|
2,800
|
|
Total Biomass Harvested (g)
|
1,270,080
|
|
Kg/m2
|
4.50
|
|
% Survival
|
91
|
|
Total Amount Fed (g)
|
1,955,525
|
|
FCR
|
1.54
|
As described above, important modifications
were made to system operations
during this trial including use
of a bead filter and removal of
solids during the backwash cycle
and injection of oxygen. Figure
1 shows the growth of the shrimp
and system dissolved oxygen levels
before and after addition of oxygen
and filtration. The apparent increase
in growth during the latter half
of the cycle is in stark contrast
to the typical plateau effect observed
in previous trials as solid levels
continued to increase late in the
growing season.
The use of oxygen can have positive benefits in terms of improved
growth and condition of the target
crop and increased system carrying
capacity, however, negative effects
of C02 buildup and associated pH
drops must be addressed.
Figure
1. Relationship between dissolved
oxygen levels and growth of Litopenaeus vannamei in a superintensive
raceway system.

Preliminary
Economic Feasibility Analysis
The
economic feasibility of commercial
shrimp culture in South Carolina
using the state
of the art indoor recirculating
biosecure systems has also been
initiated. The purpose of the analysis
is two-fold: (1) to develop bioeconomic
model specific to South Carolina
that will assist researchers in
investigating the sensitivities
of projected profits and risks
to various culture techniques and
related variables (e.g. market
prices), and (2) to provide commercial
feasibility analysis information
germane to private sector needs
(e.g. preparation of business plans).
As an initial starting point of
this analysis, a "base case" production
system along with production and
economic assumptions were selected
based upon experimental work at
the Waddell Mariculture Center
(Table 4) and other information
sources. The hypothetical, base
case production unit in the initial
analysis is comprised of five modules
each of which is comprised of six,
750/m2 raceways covered by biosecure interlinked greenhouses.
It was assumed that seawater would
be pumped in and treated from nearby
source (e.g. an estuarine creek)
and this treated seawater would
be heated via a heat exchanger
system during the colder months.
Major preliminary base case production
assumptions included direct stocking
of shrimp 1g animals at 300/m2, overall survival to harvest size of 85%, mean harvest
size of 17g, growth rate of 1.3
g/wk allowing four crops per raceway
over a 12 month period, and 1.50
FCR. Major economic assumptions
included juvenile stocking costs
of $11.50/1,000 and feed costs
of $0.50/kg. The projected total estimated cost of production
per kg is $4.36 with variable costs
making up $3.27 per kg. This preliminary analysis indicates that one
of the most important parameters
relative to reducing production
costs is growth rate. For
example maintaining growth averaging
1.44g/wk (table 4) rather than
the 1.3 g/wk in the base case scenario
would reduce projected total production
costs by $0.21 per kg. Consequently, it appears that cost-effective
techniques that can improve growth
rates such as the selection of
fast growing shrimp strains could
significantly improve the financial
performance of indoor recirculating
biosecure systems.
The WMC prototype systems provide an insight into
alternative culture technologies
that have excellent potential to
allow development and expansion
of the US shrimp farming industry.
By embracing these technologies,
the environmental impact of discharged
effluents would be reduced substantially
if not eliminated, biosecurity
protocols and procedures could
be implemented to prevent the spread
of disease agents to and from the
culture facility, and year round
culture could be achieved irrespective
of location. In addition, systems
could be located inland, potentially
near market centers, opening up
new opportunities for value added
fresh or live product sales. However,
in order for greenhouse-based minimal
exchange shrimp production systems
to be adopted commercially, they
must be proven under a research
setting to be biologically and
economically sound on a consistent
basis. To do this a commercial
scale prototype system with a minimum
of six raceways to allow for controlled
studies must be constructed such
that commercial feasibility can
be demonstrated while continuing
research and development to improve
system performance. Additional
research will be needed to explore
effects of aeration type, water
flow patterns, deployment of substrates,
diets, feeding regimes, and other
factors. Appropriate use of oxygen
supplementation, filtration, and
solids removal will require additional
replicated studies to develop optimal
protocols to assure maximum growth
and production with the highest
efficiency of protein use. Future
studies will also have to address
the disposal or treatment options
for solids removed from these superintensive
systems. Although some studies have demonstrated the
use of these solids as fertilizers
and soil amendments further research
in this area is needed. As discussed,
data obtained from previous, ongoing,
and future trials are being subjected
to appropriate economic feasibility
analyses to develop baseline cost
and return information. These data
will be reported in a separate
publication and will be used to
project profitability of various
multi-unit culture system layouts
and to drive establishment of ongoing
research objectives.
In
summary, it appears that the commercial
development of greenhouse, superintensive
shrimp culturing is favorable in
the US, but it will remain dependent
upon applied research and development
of cost-effective production techniques
coupled with marketing approaches
that can buffer US commercial shrimp
farm products from the vicissitudes
of major US shrimp market segments,
especially those segments that
are apparently subject to shrimp
import induced price reductions.
Literature Cited
Boyd, C.E.
and J.W. Clay. “Shrimp Aquaculture
and the Environement.”Scientific
American 278(6; 1998):58-65.
Boyd, C.E. and J.W. Clay. “Evaluation
of Belize Aquaculture, Ltd: a Superintensive
Shrimp Aquaculture System.”Washington,
DC. World Bank, Network of Aquaculture
Centres in Asia-Pacific, World Wildlife
Fund and Food and Agriculture Organization
of the United Nations Consortium
Program on Shrimp Farming and the
Environment.2002.
Bratvold, D. and C. L. Browdy. “Disinfection,
Community Establishment and Production
in a Prototype Biosecure Shrimp Pond.Journal
of the World Aquaculture Society 30(1999):422-432.
Brock, J. A., R. B. Gose, D. V.
Lightner, and K. Hasson.“Recent Developments
and an Overview of Taura Syndrome
of Farmed Shrimp in the Americas.”Pages
275-284 in >T. W. Flegel and I. H. McRae (editors).>Diseases in Asian Aquaculture
III. Manila, Phillipines: Fish
Health Section, Asian Fisheries Society.1997.
Browdy, C. L., D. Bratvold, A. D.
Stokes, and R. P. McIntosh. “Perspectives
on the Application of Closed Shrimp
Culture Systems.” Pages 20-34 in
C. L Browdyand D.E. Jory (editors).The
New Wave: Proceedings of the Special
Session on Sustainable Shrimp Culture,
Aquaculture 2001.Baton Rouge,
Louisiana, USA.The World Aquaculture
Society. 2001.
Davis, D. A. and C. R. Arnold.“The
Design, Management, and Production
of a Recirculating Raceway System
for the Production of Marine Shrimp.” Aquaculture
Engineering 17(1998):193-211.
Flegel, T. W., S. Boonyaratpalin,
and B. Withyachumnarnkul. “Progress
in Reseach on Yellow-Head Virus and
White-Spot Virus in Thailand.”Pages
285-295 in T. W. Flegel and I. H.
McRae (editors). Diseases in Asian
Aquaculture III.Manila, Phillippines.
Fish Health Section, Asian Fisheries
Society. 1997.
Goldburg, R. and T. Triplett.1997.Murky
Waters: Environmental Effects of
Aquaculture in the United States.Washington,
DC, USA.Environmental Defense Fund
Publications.1997.
Hopkins, J. S., M. R. DeVoe, P.
A. Sandifer, A. F. Holland, and C.
L. Browdy.“The Environmental Impacts
of Shrimp Farming with Special Reference
to the Situation in the Continental
US.” Estuaries 18(1995):25-42.
Landesman, L.“Negative impacts
of coastal aquaculture development.”World
Aquaculture 25(1994):12-17.
Leung, P. S. and S. M. Moss.>“Economic
Assessment of a Prototype Biosecure
Shrimp Growout Facility.”Pages 97-106 in R. A. Bullis and G. D. Pruder (editors).Controlled and Biosecure
Production Systems: Evolution and
Integration of Shrimp and Chicken
Models.Proceedings of a Special Session of the World Aquaculture Society, Sydney, Australia.Honolulu, Hawaii, USA.The
Oceanic Institute.1999.
Lotz. J. M. and D. V. Lightner.“Shrimp
Biosecurity: Pathogens and Pathogen
Exclusion.” Pages 67-74 in R.
A. Bullis and G. D. Pruder (editors).Controlled and Biosecure Production Systems.Proceedings of a Special Session – Integration
of Shrimp and Chicken Models.
Waimanalo, Hawaii, USA.The Oceanic
Institute.2000.
Lightner, D. V.“The Penaeid Shrimp
Viruses TSV, IHHNV, WSSV and YHV:
Current Status in the Americas, Available
Diagnostic Methods and ManagementStrategies.”Journal
of Applied Aquaculture 9(1999):27-52.
Lightner, D. V., K. W. Hasson, B.
L. White, and R. M. Redman. “Experimental
Infection of Western Hemisphere Shrimp
with Asian White Spot Syndrome Virus
and Asian Yellow Head Virus.”Journal
of Aquatic Animal Health 10(1998):271-
281.
Main, K. L. and W. Fulks.“The Culture
of Cold-Tolerant Shrimp.”Proceedings
of an Asian-US Workshop on Shrimp
Culture.Honolulu, Hawaii, USA.The
Oceanic Institute, Makapuu Point.1990.
Main, K. L. and P. Van Wyk.“Introduction.”Pages 1-5 in P. Van Wyk et al. (editors).Farming Marine Shrimp in Recirculating
Freshwater Systems.Tallahassee, Florida,
USA.Florida
Department of Agriculture and
Consumer Services.1999.
Moore, D.W. and C.W. Brand.
1993. The culture of marine shrimp
in controlled environement superintensive
systems.Pages
315-348 in: J.P. McVey, editor.
CRC Handbook of Mariculture. CRC
Press, Boca Raton, FL, USA.
>Moss, S. M.“Biosecure
Shrimp Production: Emerging Technologies
for a Maturing Industry.”Global
Aquaculture Advocate 2(4/5;
1999):50-52.
Moss, S. M., S. M. Arce, B. J. Argue, C. E. Otoshi,
F. R. O. Calderon, and A. G. J. Tacon.“Greening of the Blue Revolution: Efforts
Toward Environmentally Responsible
Shrimp Culture.”Pages
1-12 in C. L. Browdy and D. E. Jory (editors).The New Wave: Proceedings
of the Special Session on Sustainable Shrimp
Culture, Aquaculture 2001.Baton
Rouge, Louisiana, USA.The
World Aquaculture Society.2001.
Ogle, J. T. and J. M. Lotz.“Preliminary Design of a Closed, Biosecure
Shrimp Growout System.”Pages 39-48 in S. M. Moss (editor).U.S. Marine Shrimp Farming Program Biosecurity Workshop.Honolulu, Hawaii, USA.The Oceanic Institute.1998.
Rhodes, R.J., S. Sureshwaran, C. Greene, C.L. Browdy, J.D. Holloway, and
T.M. Samocha. “Production Effects
of a Greenhouse Enclosed Nursery
System on the Projected Financial
Performance of a South Carolina Marine
Shrimp Farm.” Technical Report No.
85, Charleston, South Carolina, USA.
Marine Resources Division, South
Carolina Department of Natural Resources,
1995.
Samocha,
T. M., L. Hamper, C. R. Emberson,
A. D. Davis, D. McIntosh, A. L. Lawrence,
and P. M. Van Wyk. 2002.“Review
of Some Recent Developments in Sustainable
Shrimp Farming Practices in Texas,
Arizona and Florida.Journal
of Applied Aquaculture 12(1; 2002):1-42.
Scarpa, J. “Freshwater
Recirculating Systems in Florida.”in S. M.
Moss (editor).Proceedings
of the US Marine Shrimp Farming
Program Biosecurity Workshop.Honolulu,
Hawaii, USA.The
Oceanic Institute.1998.
Van Wyk, P.“Designing
Efficient Indoor Shrimp Production
Systems: a Bioeconomic Approach.”Pages
44-56 in C.
L Browdy and D. E. Jory (editors).The
New Wave: Proceedings of the Special
Session on Sustainable Shrimp Culture,Aquaculture
2001.Baton
Rouge, Louisiana, USA.The
World Aquaculture Society.2001.
Van Wyk, P.“Culture
of Penaeus vannamei in Single-Phase
and Three-Phase Recirculating Aquaculture
Systems.” Global Aquaculture Advocate
343. Van Wyk, P.“Harbor
Branch Shrimp Production Systems.”Pages 99-114 in P.
Van Wyk
et al. (editors).Farming
Marine Shrimp in Recirculating
Freshwater Systems.Tallahassee,
Florida, USA. Florida
Department of Agriculture and Consumer
Services. 1999.
Van Wyk, P. and J. Scarpa. “Water Quality Requirements and Management.” Pages 128-138 in P.
Van Wyk et al. (editors). Farming
Marine Shrimp in Recirculating Freshwater
Systems. Tallahassee,
Florida, USA. Florida
Department of Agriculture and Consumer
Services. 1999.
Weirich
C.R., Bratvold D., Browdy C.L., and
B.J. McAbee. Abstract. “Preliminary
evaluation of emerging water treatment
technologies for use inminimal
exchange super-intensive pacific
white shrimp
normal'>Litopenaeus vannamei culture systems.” Aquaculture
America’ 2003, Louisville, KY February 18-21. Pg. 318.
Weirich
C.R., C.L. Browdy, D. Bratvold, B.J.
McAbee, and A.D. Stokes. “Preliminary
characterization of a prototype minimal
exchange super-intensive
shrimp
production system. Proceedings of the Ivth International Conference on Recirculating Aquaculture, Virginia Tech
University, Blacksburg, VA, July 2002. Pg
255-270.
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