TABLE OF CONTENTS Pages Symposium 1 - the National Sea ...

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Introduction Implications of Total Maximum Daily Load (TMDLs) on Aquaculture Charles H. Martin Environmental Engineer Consultant, Office of Water Quality Assessments, Virginia Department of Environmental Quality Total Maximum Daily Loads or TMDLs are required by §303(d) of the Clean Water Act (CWA) and the §4.01 of Virginia’s State Water Control Law. The state statute is known as the Water Quality Monitoring, Information and Restoration Act. The first requirement of §303(d) of the CWA is that the states identify and develop a list of impaired waters (those not meeting water quality standards). The second requirement is that the states develop TMDLs for waters on the 303(d) lists. As with most new programs, the TMDL process has produced a number of issues that impact other water quality management programs such as water quality standards, monitoring, and VPDES permits. Waters Needing TMDLs Only waters that violate Virginia’s Water Quality Standards are placed on the 303(d) List for TMDL development. These are waters that have documented long term quality problems based on chemical and biological water quality data. DEQ does not list waters for TMDL development based on temporary or transient violations of the standards. Violations of the standards are determined by the biennial analysis of the previous five years of chemical and biological water quality data from about 1,500 monitoring stations operated by DEQ, U.S. Geological Survey, and Tennessee Valley Authority (TVA). TMDLs are special studies that identify each significant source of pollution, calculate the amount of pollutant contributed by each source, and quantify the reductions needed to attain water quality standards. TMDLs are pollutant specific and waters impaired for more than one pollutant need a TMDL developed for each pollutant. Every TMDL has a point source and nonpoint source component plus a margin of safety to account for uncertainties in the TMDL analysis. The point source or nonpoint source component may be insignificant in a particular TMDL, but both components must be addressed. Virginia’s 1996 and 1998 303(d) TMDL Priority List identified streams immediately downstream of 6 fish farms as impaired due to degradation of the benthic communities. A special study funded by DEQ identified total suspended solids as the cause of the impairment. The fish farms were suspected as a significant source of the impairment. DEQ has contracted with the Virginia Water Resources Research Center to develop TMDLs for these impaired 1
stream segments. These 6 TMDLs are scheduled to be completed and submitted to EPA by May 1, 2002. These will be the first group of TMDLs developed in Virginia addressing benthic community degradation. The benthic TMDLs present special challenges in determining the cause and effect relationships between the pollutant(s) and the bottom dwelling aquatic life. Rapid Changes in TMDL Process EPA proposed on August 23, 1999, significant modifications to the TMDL regulation with associated revisions to the NPDES and the Water Quality Standards program regulations. Recently, EPA announced that the final 303(d) rules will be issued in late June or July. Apparently, EPA will proceed with an expanded TMDL program that will broaden federal authority and make the TMDL a primary water quality management program instead of just one part of the process. One of the major impacts to the TMDL regulation revisions is the requirement that an implementation plan must be submitted to EPA as a part of each TMDL. 2
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TABLE OF CONTENTS i Pages Symposium
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iii Pages Production of YY Male Til
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v Pages Special Session 2 - Volunte
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into the grow-out tanks. The airlif
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one above the other, reducing the
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nutritional requirements of summer
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Pump Functions The AMI Multi-Functi
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Introduction Commercial Application
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System Performance: Nine of these r
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electrical costs reduced by more th
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Nitrate, as the final product of th
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Culture conditions On August 1, 199
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surface area 740 m 2 /m 3 ). The co
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achieved a 750 mg/l decline in the
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ecomes possible without water repla
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tropical countries for tropical fis
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fastest absorption of nutrients fro
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Recirculation System Design; The KI
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The Japanese Aquaculture Market and
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Entrepreneurial and Economic Issues
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Our largest error though was in not
Page 43 and 44: Before You Invest. In my role as a
Page 45 and 46: are 590,000 kg/year. Prices, deprec
Page 47 and 48: Twenty-One Years of Commercial Reci
Page 49 and 50: have projects in the planning stage
Page 51 and 52: As the upward trend for seafood dem
Page 53 and 54: and the World Health Organization (
Page 55 and 56: Abstract not available at time of p
Page 57 and 58: increase the potential for bottlene
Page 59 and 60: Figure 1: Comparison of First, Seco
Page 61 and 62: Ecological and Resource Recovery Ap
Page 63 and 64: Acid mine drainage (AMD) is widespr
Page 65 and 66: and the polyphenol content (Northup
Page 67 and 68: References CAST. 1996. Integrated A
Page 69 and 70: Tilapia and Fish Wastewater Charact
Page 71 and 72: In comparison of gravity separation
Page 73 and 74: NY DEC Interaction. The owners of F
Page 75 and 76: O 2 Feed CO 2 Ammonia Figure 1. Gen
Page 78 and 79: The Hatchery The hatchery supports
Page 80 and 81: in crayfish populations, disappeara
Page 82 and 83: Table 2. Summary of average flows a
Page 84 and 85: depth decreases. Improvements in tr
Page 86 and 87: Perspective on the Role of Governme
Page 88 and 89: unprecedented in the growth of a ne
Page 90 and 91: with siting and the special equipme
Page 92 and 93: disease. We need to create environm
Page 96 and 97: The NOAA/DOC Aquaculture Initiative
Page 98 and 99: Future Directions for the NOAA/DOC
Page 100 and 101: ’ Conduct research and help devel
Page 102 and 103: Information sources for aquaculture
Page 104 and 105: Tilapia is an important fish specie
Page 106 and 107: To determine the RSE of the examine
Page 108 and 109: Fig.1(a) Typical integrated olfacto
Page 110 and 111: Table 1. Relative stimulatory effic
Page 112 and 113: feeder control algorithms on a PC s
Page 114 and 115: Durant, M. D., Summerfelt, S. T., H
Page 116 and 117: The Effects of Ultraviolet Filtrati
Page 118 and 119: Table 1. The mean (N = 20) initial
Page 120 and 121: Introduction Evaluation of UV Disin
Page 122 and 123: Figure 1 Schematic of the experimen
Page 124 and 125: Table 1 Summary of the tested resul
Page 126 and 127: similar disinfection efficiency. Th
Page 128 and 129: (2) UV254 transmittance was an impo
Page 130 and 131: Materials and Method Schematic draw
Page 132 and 133: the amount of added increase by pro
Page 134 and 135: Oxygen Management at a Commercial R
Page 136 and 137: the outlet and inlet DO concentrati
Page 138 and 139: daylight hours averaged 0.5 kg DO/k
Page 140 and 141: At this time, the control (both tan
Page 142 and 143: yellow color, while the water in th
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Case Study: Genetic improvement of
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and human effort. This commitment m
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- Harold Kincaid works for the US F
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Figure 1. Production and selection
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Performance Comparison of Geographi
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Abstract Issues in the Commercializ
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The Salmon Example Salmon farming i
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Second, as the salmon farming indus
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Devlin, R.H., Yesaki, T.Y., Biagi,
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Introduction Removal of Protein and
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higher superficial air velocity gre
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Hydrodynamics in the ‘Cornell-Typ
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The ideal mean residence time was a
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A sample pellet-flushing test is sh
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tank’s dead time. When fish were
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Partial-Reuse Systems Ideally, the
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Figure 1. The partial-recirculating
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Table 1. Mean values (± standard e
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dioxide (1) and un-ionized ammonia
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Comparative Growth of All-Female Ve
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Effects of Temperature and Feeding
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aquaculture systems, where the envi
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Figure 2. Growth relationships of y
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greater than the desired temperatur
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Figure 3. Cumulative feed consumpti
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35 days into the experiment, and th
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C. Maximum specific feed consumptio
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of the fish used in this experiment
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Coche, A.G. Cage culture of tilapia
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Predictive Computer Modeling of Gro
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new studies begun. Daily water qual
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Development Rationale for the Use o
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Further, reduction in operating cos
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The operation of the MRBF is domina
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equired a high frequency of washing
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Several dramatically different hull
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support airlift applications. These
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Enhancing Nitrification in Propelle
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The last filter media used in this
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Table 2. Water quality analyses wer
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1193.67 g-NO2 m -3 d -1 with the ni
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Biofilters Used in Recirculating Fi
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The Cyclone Sand Biofilter: A New D
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Marine Biotech (Beverly, MA) 2 has
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120.0% 100.0% 80.0% 60.0% 40.0% 20.
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Nitrification Potential and Oxygen
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diffused aeration. The experiments
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It needs to be pointed out that the
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ammonia removal rate was low in the
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Tanaka, H. and Dunn, I. 1982. Kinet
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Ammonia removal activity was increa
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Ammonia Conc. (mg/NH 4 + -N/L) 12 1
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Antifouling Sensors and Systems for
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The Vic Thomas Striped Bass Hatcher
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Introduction In the Central Valley
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Each of the two recirculation syste
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Body injury rates (% of fish) to th
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usiness expectations and limited te
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needs of the endemic Murray-Darling
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sold (Gooley et al. 1999). The dist
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In response to the large levels of
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planning at the outset will, more t
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Table 1 Summaries of selected speci
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a) Photo courtesy of Neil Armstrong
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Information flow 1. Initial concept
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achieve continuous production, faci
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Solids Removal (9.71%) Electricity
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The Effect of Fish Biomass and Deni
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Marine Denitrification of Denitrifi
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(a) (b) (c) Nitrate conc. (mg NO 3
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6. Poxton, M. G. and S. R. Allouse.
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control unit. Two distinct advantag
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the many variables that are involve
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Filtration Recirculation systems re
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6. AERATION DEVICE: 6” airstones
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Piper, R.G., I.B. McElwain, L.E. Or
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carried out for both the 50 m 3 and
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possible to predict mean monthly ta
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Recirculation Systems for Farming E
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of this pilot-system will be evalua
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Figure 2. The main screen of the en
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What: What is your business structu
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should more than offset the costs o
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• Any other documents indicating
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production projects. Once these par
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A single discharge pipe works to re
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1. Oxygen recharge rates or the abi
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2.9.1.2. Measure ammonia. 2.9.1.3.
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Discharge pipe Number used within e
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Previous efforts by the Illinois De
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media. The water enters the filter
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Table 3: Summary of pro forma cash
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References Moss, S.M. (1999) “Bio
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Propagation and Culture of Endanger
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at a rate of 2 ft 3 /kg feed/d. Sod
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Modification of D-Ended Tanks for F
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MATERIALS AND METHODS All tests wer
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The single 100 ppm hydrogen peroxid
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The Potential for the Presence of B
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The main advantage for microorganis
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organism causes disease in humans,
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Bacteria No. of Facilities No. of D
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Assanta, M.A., Roy, D. and Montpeti
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Jones, K. and Bradshaw, S.B. (1996)
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Wilderer, P.A. and Characklis, W.G.
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systems (Egusa, 1981; Mellergaard a
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ecirculating system after mortality
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Fish Health Monitoring and Maintena
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disease problems. For tilapia, a sp
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The Role of Fish Density in Infecti
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This apparent interaction between t
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References Banks, J.L. (1994) Racew
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