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EPA's Vessel General Permit and Small Vessel General

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Table 21. Estimated Stern Tube Packing Gl<strong>and</strong> Effluent Pollutant Concentrations used in<br />

EPAs Biological Evaluation.<br />

Pollutant<br />

Point<br />

Estimate<br />

Used in<br />

BE<br />

Detection<br />

Frequency Mean (range) 50th /75 th /90 th<br />

Percentiles b<br />

Total Phosphorus (mg/L) 0.13 7/9 0.13 (nd a -0.25) 0.1/0.22/0.25<br />

Total Suspended Solids (TSS, mg/l) 59 9/9 59 (5.6-270) 28/81/270<br />

Hexane Extractable Material (HEM, mg/l) 14 5/9 14 (nd-67) 1.65/23/67<br />

Chromium, (dissolved, μg/L) 13 5/9 19 (nd-110) 3.8/20/110<br />

Silica Gel Treated HEM (SGT-HEM, mg/l) 19 5/9 13 (nd-56) 1.7/19/56<br />

Copper (dissolved, μg/L) 22 4/9 22 (nd-92) nc c /38/92<br />

Nickel (dissolved, μg/L) 210 6/9 210 (nd-1000) 13/370/1000<br />

Nickel (total, μg/L) 610 8/9 610 (nd-3200) 45/970/3200<br />

Bis (2-ethylhexyl)phthalate (μg/L) 4.7 3/9 4.7 (nd-24) nc/4.1/24<br />

Tetrachloroethene (μg/L) 1.4 1/9 1.4 (nd-0.2) nc/nc/0.2<br />

a<br />

Nondetect (censored) concentrations were replaced with ½ of the reporting limit for calculating average<br />

concentrations.<br />

b<br />

Percentiles are the concentrations of each analyte below which at least that percentage of the values fall.<br />

So the 75th percentile is the concentration below which at least 75% of the observations were found.<br />

c<br />

Distribution statistics were only calculated when analytes were detected at a sufficient frequency.<br />

Underwater Ship Husb<strong>and</strong>ry Discharges. Although discharges from underwater ship<br />

husb<strong>and</strong>ry is considered a low volume <strong>and</strong> low frequency discharge generated by a low number<br />

of vessels, EPA analyzed the risk of this discharge in its BE due to the high potential risk posed<br />

by the concentration <strong>and</strong> types of pollutant discharged. Underwater husb<strong>and</strong>ry discharge<br />

volumes were not estimated because EPA was unable to find available data to accurately<br />

estimate volume of these discharges. Furthermore, EPA round approached ANS risk<br />

qualitatively, so volume estimates were not necessary. EPA’s Report to Congress did provide<br />

copper release estimates for underwater ship husb<strong>and</strong>ry events (Table 22).<br />

Table 22. Dissolved Copper Release from <strong>Vessel</strong> AFSs During an Underwater Hull<br />

Cleaning “Event” (Schiff et al. 2003, after USEPA 2010).<br />

AFS Cleaning Method<br />

Epoxy copper<br />

antifouling paint<br />

Hard vinyl/Teflon<br />

copper antifouling<br />

paint<br />

Biocide-free coating<br />

Copper Release<br />

(μg/cm2/event)<br />

Less abrasive management practices 8.6<br />

No management practices 17.4<br />

Less abrasive management practices 3.8<br />

No management practices 4.2<br />

Less abrasive management practices 0.03<br />

No management practices 0.05<br />

257

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