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AgdaPkt 2016-02-22 Closed and Interview and Joint SA PFA
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AgdaPkt 2016-02-22 Closed and Interview and Joint SA PFA
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2/23/2016 8:19:52 AM
Creation date
2/18/2016 3:58:00 PM
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CC Index
CC Index - Document Type
Agenda Packet
Meeting Type
Joint
Agency Type
City Council and Successor Agency and Public Financing Authority
Date
2/22/2016
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City of Redwood City, Public Works Division Initial Study & Mitigated Negative Declaration <br />Document Date: October 15, 2015 <br />Revision Date: January 25, 2016 Page 30 Blankinship & Associates, Inc. <br /> <br />interspecies differences in copper toxicity (Grosell et al., 2007). Thus, similarity in size <br />between the test organism and longfin smelt was an important consideration in the selection of <br />an endpoint for TRV derivation. Additionally, test conditions, such as salinity and duration of <br />exposure, were also considered in the selection process. <br /> <br />After a substantial literature review, the 96-hour acute LC50 of 86.5 mg/L was selected from <br />the following study as the endpoint used for TRV Derivation: <br /> <br />Mohapatra and Rengarajan 1997 <br />The acute toxicity of copper to wild-caught Liza parsia was evaluated. Liza parsia weighing <br />between 15.0 to 30.0 grams (g) and measuring between 75.0 to 105.0 mm (approximately 3 to <br />4 inches) total length were collected from the brackish water canals of Puduvypeen area in <br />Cochin. The fish were acclimatized to laboratory conditions for about one week at an <br />approximate salinity of 9.8 parts per thousand (ppt), temperature of 28 °C, and total hardness <br />of 2,956 ppm. Fish were exposed to copper sulfate pentahydrate in 5 separate aquarium <br />bioassays to estimate the 12, 24, 48, 72, and 96 hour toxicity of copper. The metallic copper <br />LC50 estimated for the 12, 24, 48, 72, and 96 hour bioassays were 35.9, 34.9, 28.0, 22.0, and <br />21.8 mg/L, respectively. We selected the 96 hour LC50 of 21.8 mg/L, consistent with acute <br />endpoint selection recommendations (USEPA 2004). <br /> <br />To derive a TRV from the 96 hour LC50, a safety factor of 20 was applied. The resultant <br />derived TRV for the longfin smelt is estimated at 1.09 mg/L (i.e. 21.8 / 20 = 1.09) . It was <br />estimated that applications of copper at the maximum label rate of 1.0 mg/L metallic copper <br />will not lead to aquatic exposure greater than or equal to the derived aquatic TRV of 1.09 mg/L <br />because the calculated risk value is 0.917 (unitless). The copper-containing algaecides and/or <br />aquatic herbicides applied to the Lagoon are not anticipated to pose unacceptable risk to <br />longfin smelt. <br /> <br />To educate City or contractor staff working in the Lagoon of the potential presence of longfin <br />smelt, a qualified biologist shall conduct a worker’s environmental awareness program <br />(WEAP). The WEAP training will be completed prior to application of aquatic herbicides <br />containing copper to control vegetation in the Lagoon. The WEAP will include, at a minimum, <br />species identification, a description of suitable habitat for the species, and measures to <br />implement in the event that this species is found during application. This training shall instruct <br />personnel to recognize longfin smelt their habitats and life history. <br /> <br />As described above, no unacceptable acute risk to the longfin smelt is anticipated due to <br />applications of copper-containing algaecides and/or aquatic herbicides. A qualified biologist <br />will conduct a WEAP training session prior to the application of copper-containing algaecides <br />or aquatic herbicides to the lagoon after the City’s SIP Exception is granted. <br /> <br />Item b): No Impact. The Project will take place in the Lagoon, therefore, will not impact any <br />riparian habitat or other sensitive natural community identified in local or regional plans, <br />policies, or regulations, or by the California Department of Fish and Wildlife or U.S. Fish and <br />Wildlife Service. <br /> <br />Item c): No Impact. The Project will take place in the Lagoon and, therefore, will not impact any <br />upland habitat or wetlands. However, the assessment of risk for species that live in these <br />areas was considered. Specifically, the risk to longfin smelt was assessed and it was <br />concluded that the use of aquatic herbicides containing copper does not pose an unacceptable <br />risk to the species. <br />6.3.A. - Page 38
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