EPA's Vessel General Permit and Small Vessel General

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Table 16. Fish Hold Effluent and Cleaning Effluent Discharge Rates (USEPA 2010). Commercial Fishing Vessel Type Estimated Fish Hold Effluent Discharge Rate Gillnetter 0.80 211 Lobster Boat 2.83 748 Longliner 2.83 748 Estimated Fish Hold Cleaning Effluent Discharge Rate m 3 /day gal/day m 3 /day gal/day Purse Seiner 16.3 4,306 1.07 283 Shrimper 1.25 330 Tender 19.3 5,099 0.66 174 Trawler 1.25 330 0.22 58 Troller 3.04 803 0.66 174 EPA estimated concentrations of fish hold and fish hold cleaning effluent pollutants based on data for the vessel types examined in the Report to Congress (Table 17). Contaminants identified in fish hold and fish hold cleaning effluent include metals and volatile/semivolatile organic chemicals (sVOCs/VOCs). 252
Table 17. Estimated Fish Hold and Fish Hold Cleaning Effluent Pollutant Concentrations used in EPAs Biological Evaluation. Fish Hold Effluent Fish Hold Cleaning Effluent Pollutant BE Point Estimate Detection Frequency Mean (range) 50th /75 th /90 th Percentile b BE Point Estimate Detection Frequency Mean (range) 50th /75 th /90 th Percentile Ammonia Nitrogen 12 25/26 12 (nd a -160) 2.1/6.7/160 16 7/9 16 (nd-97) 4.8/18/97 Total Phosphorous 13 25/26 13 (nd-76) 9.7/17/76 8.5 7/9 8.5 (nd-20) 11/17/20 Total Residual Chlorine 0.096 10/26 0.096 (nd-0.3) nc c /0.13/0.3 0.29 6/9 0.29 (nd-1.5) 0.11/0.29/1.5 Total Suspended Solids (TSS) 210 26/26 210 (10-1100) 130/190/1100 190 9/9 190 (16-460) 84/400/460 Biochemical Oxygen Demand (BOD) 840 24/26 840 (nd-5100) 440/830/5100 470 6/9 470 (nd-1800) 300/770/1800 Hexane Extractable Oil and Grease (HEM) Silica Gel Treated-Hexane 3.2 18/26 3.2 (nd-16) 1.5/2.9/16 5.4 6/9 5.4 (nd-28) 1.4/4.2/28 Extractable Oil and Grease (SGT-HEM) 3.4 15/26 3.4 (nd-4.4) 0.98/2.2/4.4 4.9 4/9 4.9 (nd-12) nc/2.8/12 Aluminum (total) 827 24/26 490 (nd-1000) 670/850/1000 1100 9/9 1100 (850- 1700) 930/1500/1700 Arsenic (dissolved) 31 10/26 31 (nd-350) nc/5.7/350 22 5/9 22 (nd-97) 5.3/38/97 Arsenic (total) 40 16/26 40 (nd-380) 4.8/13/380 35 5/9 35 (nd-150) 8.7/64/150 Cadmium (dissolved) 0.77 1/26 0.77 (nd-1.4) nc/nc/1.4 Copper (dissolved) 96 23/26 96 (nd-920) 15/38/920 34 8/9 34 (nd-180) 12/32/180 Lead (dissolved) 0 3/26 2.3 (nd-8) nc/nc/8 2.7 1/9 2.7 (nd-8.7) nc/nc/8.7 Selenium (dissolved) 9.2 6/26 9.2 (nd-61) nc/2.5/61 6 1/9 6 (nd-14) nc/nc/14 Zinc (dissolved) 180 26/26 180 (24-790) 120/240/790 190 8/9 190 (nd-640) 53/420/640 a Nondetect (censored) concentrations were replaced with ½ of the reporting limit for calculating average concentrations. b Percentiles are the concentration below which that percentage of the values fall. So 75 percent of observations occur below the 75th percentile. c Distribution statistics were only calculated when analytes were detected at a sufficient frequency. 253
Page 1 and 2:
Endangered Species Act Section 7 Co
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Rockfish ..........................
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LIST of TABLES Table 1. Species Lis
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Agency: Activities Considered: Nati
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allast water volume. They also agre
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� Distillation and Reverse Osmosi
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� Conduct fueling in a manner tha
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stability of the ship. Any discharg
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� Annual calibration of ballast w
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The discharge of Tributyltin (TBT)
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For vessels covered under the VGP,
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For vessels covered under the VGP,
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waters (Appendix G, VGP). Non-Oily
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� Limiting use of hard brushes an
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adjusted upward for lower washwater
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� Dispose of the graywater at an
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� Appropriate reprimand procedure
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Under the VGP, the EPA authorizes t
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� Ensuring material storage, and
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2. Voyage Log. Include the dates an
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tanks in ballast. Use units of meas
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USC §1001 or 18 USC §1519. To mon
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discharges to an impaired water wit
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� Prevent monofilament line, fish
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Ballast Water. For vessels covered
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submitted or required to be maintai
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� Use soaps and detergents that a
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eports in time to make changes for
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for these components of an action);
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Regardless of whether an agency’s
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suspected to produce physical, phys
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Response Analyses We conduct a deta
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iotic phenomena to a degree that wo
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seaward a distance of three miles.
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Table 1. Species Listed as Threaten
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Based upon our analyses, we conclud
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11. Certain park pest management ac
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alter macroinvertebrate communities
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support one or more Chinook salmon
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quality growth, reproduction, and f
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quality and quantity, natural cover
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occurs in residence time in fresh w
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This ESU consists of a single spawn
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Status and Trends NMFS originally l
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Critical Habitat NMFS designated cr
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support one or more Chinook salmon
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Most of the chum within this ESU re
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On average Hood Canal chum salmon r
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estuaries and in fresh water coho s
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FR 24049). The designation encompas
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100,000 fish by the mid-1960s with
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1996). However, the decline in prod
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other tributaries flowing into Ozet
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Status and Trends Snake River socke
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parts of pools, while winter rearin
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Creek, Waddell Creek, Gazos Creek,
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1996). Steelhead in these basins tr
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Cowlitz Trout Hatchery winter-run p
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White Salmon River and Deschutes Cr
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Status and Trends NMFS listed North
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summer-run fish, comprising 37 of t
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status as threatened on January 5,
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elow the dam and the older dam coun
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extirpated due to dewatering or bar
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to 3,714 while naturally produced s
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The smolt migration past Willamette
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Movement, growth, and reproduction
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date, Atlantic salmon are listed in
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1997, Somero and Hofmann 1997, Van
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Southern Pacific Eulachon Eulachon
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Threats Natural Threats. Birds and
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are low in comparison to catch leve
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Female shortnose sturgeon spawn eve
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Anthropogenic Threats. Historic fis
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of all life stages in the riverine
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adults generally migrate upriver in
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Bocaccio are live-bearers with inte
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ycatch and habitat loss are also hu
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historical population in the Strait
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During each annual spawning event,
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Caribbean and Central America, the
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occur regularly in waters in excess
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Natural threats The primary natural
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diets (Reich et al. 2010, Vander Za
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fish, jellyfish, mollusks, and tuni
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sea turtle survival and recovery in
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Leatherback sea turtle (Dermochelys
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in leatherbacks and can block gastr
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the population has experienced a co
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Strandings may represent a signific
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eulachon, Pacific cod, walleye poll
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which makes it potentially vulnerab
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North Atlantic right whales exhibit
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impeded by competition with other w
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Southern Oceans. Most populations m
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Nemoto 1959, Nemoto 1970, Krieger a
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Natural threats The overriding thre
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planktonic larvae form before settl
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than 12% on many reefs (Rogers et a
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Critical habitat NMFS published a f
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Natural threats Natural pressures e
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Black abalone have also experienced
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2009). The largest known groups of
Page 208 and 209: areas compared to historical condit
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Page 212 and 213: another 2.5 to 4°F during the wint
Page 214 and 215: Table 2. Phenomena associated with
Page 216 and 217: In addition to these changes, clima
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Page 220 and 221: Effects of the Action The Effects o
Page 222 and 223: fuel barges, crane barges, dry bulk
Page 224 and 225: and only 3% of emergency vessels ar
Page 226 and 227: propeller) to create thrust and det
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Page 230 and 231: � Minimize the transport of any v
Page 232 and 233: information about the distribution
Page 234 and 235: The uptake and discharge of ballast
Page 236 and 237: quantify the annual number of newly
Page 238 and 239: Stressors Established ANS are stres
Page 240 and 241: autochthonous gross primary product
Page 242 and 243: damage to mortality. Baleen whales
Page 244 and 245: While there are many examples of fr
Page 246 and 247: skeleton that is free from fleshy o
Page 248 and 249: VGP Authorized Discharge sVGP Autho
Page 250 and 251: for large cruise ships. The example
Page 252 and 253: EPA used information for commercial
Page 254 and 255: Aluminum, Total (μg/L) Cadmium, Di
Page 256 and 257: Exhaust Gas Scrubber Washwater Effl
Page 260 and 261: Graywater and Graywater Mixed with
Page 262 and 263: include controllable pitch propelle
Page 264 and 265: Discharges not Evaluated in the BE.
Page 266 and 267: Table 23. Decision Process for thos
Page 268 and 269: Table 23. Decision Process for thos
Page 270 and 271: Estimates of Exposure Resulting fro
Page 272 and 273: For the fraction of freshwater mode
Page 274 and 275: Table 26. Estimated Receiving Water
Page 280 and 281: Geographical Distribution and Overl
Page 282 and 283: Bocaccio (Sebastes paucispinis), Ca
Page 284 and 285: mg/L (USEPA 2008). Average phosphor
Page 286 and 287: esponse follows a “one hit” mod
Page 288 and 289: species. (Glazebrook and Campbell 1
Page 290 and 291: from large cruise vessels. The sour
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Page 294 and 295: physiological damage to the recepto
Page 296 and 297: the original estimates (USEPA 2012a
Page 298 and 299: on reproduction and survival would
Page 300 and 301: Table 33. Application of the Ecosys
Page 302 and 303: metabolism of organic chemicals. Wh
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Page 306 and 307: than EPA’s HC5 TLM for benzo(a)py
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A later study by the same workers r
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(1) Scope In this section, we ask w
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estimate whether those discharges h
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analyzed due to a lack of resources
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concentration calculated for the hy
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Annually, EPA will collect and revi
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methodologies and understanding of
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traditionally requires applying dat
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In conclusion, the Service evaluate
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The VGP requires that vessel operat
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justified the application of signif
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Integration and Synthesis The EPA p
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population and a competitor could e
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Second, EPA will monitor pollutants
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is incidental to and not intended a
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minimize or avoid adverse effects o
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Adey, W. H. 1978. Coral reef morpho
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acidification causes bleaching and
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State University, Arcada, Californi
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and high-use areas of western Pacif
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Blum, J. P. 1988. Assessment of fac
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(Special Issue) 2:245-250. Browning
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Conservation 78:97-106. Carlton, J.
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River-specific target spawning requ
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pinniger in Canada. Committee on th
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comparison of reef maps from 1881 a
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Dustan, P. 1985. Community structur
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Erickson, D. L. and J. E. Hightower
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(Eubalaena glacialis). Aquatic Mamm
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Gilmore, M. D. and B. R. Hall. 1976
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London. Groot, C. and L. Margolis.
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Hanson, B., R. W. Baird, and G. Sch
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HDLNR. 2002. Application for an ind
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trawl fishery 1962-64. Washington D
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Comprehensive Guide to their Identi
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Yellowstone Ecosystem. Journal of t
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San Juan archipelago. Washington De
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Littell, J. S., M. M. Elsner, L. C.
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American Meteorological Society 78:
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and D. G. McDonald, editors. Global
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Mieog, J. C., J. L. Olsen, R. Berke
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Moser, H. G. 1967. Reproduction and
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offshore waters of the North Pacifi
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NMFS. 2008d. National Marine Fisher
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polycyclic aromatic hydrocarbons. E
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pectinata (Elasmobranchiomorphi: Pr
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(Lepidochelys kempii). Journal of H
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T. B. B. Smith, R., C. F. G. Jeffre
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Margolis, editors. Pacific Salmon L
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36:447-453. Seminoff, J. A., A. Res
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idley sea turtles: Evidence from ma
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Marine Ecology-Progress Series 377:
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Quality Criteria for Oil and Grease
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Veracruz, Mexico. United States Fis
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Virnstein, R. W. and L. J. Morris.
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Scotian Rivers have not declined in
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Williams, R., D. E. Bain, J. K. B.
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under the Endangered Species Act. W
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