A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power Plant

A study to determine the effects of entrainment by the Diablo Canyon Power Plant (DCPP) was conducted between 1996 and 1999 as required under Section 316(b) of the Clean Water Act. The goal of this study was to present the U.S. Environmental Protection Agency (EPA) and Central Coast Regional Water Q...

Full description

Bibliographic Details
Main Authors: C.P. Ehrler, J.R. Steinbeck, E.A. Laman, J.B. Hedgepeth, J.R. Skalski, D.L. Mayer
Format: Article
Language:English
Published: Hindawi Limited 2002-01-01
Series:The Scientific World Journal
Online Access:http://dx.doi.org/10.1100/tsw.2002.182
id doaj-128c32eeca3d47039bc59c1ec834e67b
record_format Article
spelling doaj-128c32eeca3d47039bc59c1ec834e67b2020-11-25T00:30:59ZengHindawi LimitedThe Scientific World Journal1537-744X2002-01-0128110510.1100/tsw.2002.182A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power PlantC.P. Ehrler0J.R. Steinbeck1E.A. Laman2J.B. Hedgepeth3J.R. Skalski4D.L. Mayer5Tenera Environmental, 225 Prado Road, Suite D, San Luis Obispo, CA, 93401, USATenera Environmental, 225 Prado Road, Suite D, San Luis Obispo, CA, 93401, USATenera Environmental, 225 Prado Road, Suite D, San Luis Obispo, CA, 93401, USATenera Environmental, 225 Prado Road, Suite D, San Luis Obispo, CA, 93401, USAColumbia Basin Research, 1325 Fourth Ave., Suite 1850, Seattle, WA, 98101-2509, USATenera Environmental, 100 Bush Street, Suite 850; San Francisco, CA, 94104, USAA study to determine the effects of entrainment by the Diablo Canyon Power Plant (DCPP) was conducted between 1996 and 1999 as required under Section 316(b) of the Clean Water Act. The goal of this study was to present the U.S. Environmental Protection Agency (EPA) and Central Coast Regional Water Quality Control Board (CCRWQCB) with results that could be used to determine if any adverse environmental impacts (AEIs) were caused by the operation of the plant’s cooling-water intake structure (CWIS). To this end we chose, under guidance of the CCRWQCB and their entrainment technical working group, a unique approach combining three different models for estimating power plant effects: fecundity hindcasting (FH), adult equivalent loss (AEL), and the empirical transport model (ETM). Comparisons of the results from these three approaches provided us a relative measure of confidence in our estimates of effects. A total of 14 target larval fish taxa were assessed as part of the DCPP 316(b). Example results are presented here for the kelp, gopher, and black-and-yellow (KGB) rockfish complex and clinid kelpfish. Estimates of larval entrainment losses for KGB rockfish were in close agreement (FH is approximately equals to 550 adult females per year, AEL is approximately equals to 1,000 adults [male and female] per year, and ETM = larval mortality as high as 5% which could be interpreted as ca. 2,600 1 kg adult fish). The similar results from the three models provided confidence in the estimated effects for this group. Due to lack of life history information needed to parameterize the FH and AEL models, effects on clinid kelpfish could only be assessed using the ETM model. Results from this model plus ancillary information about local populations of adult kelpfish suggest that the CWIS might be causing an AEI in the vicinity of DCPP.http://dx.doi.org/10.1100/tsw.2002.182
collection DOAJ
language English
format Article
sources DOAJ
author C.P. Ehrler
J.R. Steinbeck
E.A. Laman
J.B. Hedgepeth
J.R. Skalski
D.L. Mayer
spellingShingle C.P. Ehrler
J.R. Steinbeck
E.A. Laman
J.B. Hedgepeth
J.R. Skalski
D.L. Mayer
A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power Plant
The Scientific World Journal
author_facet C.P. Ehrler
J.R. Steinbeck
E.A. Laman
J.B. Hedgepeth
J.R. Skalski
D.L. Mayer
author_sort C.P. Ehrler
title A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power Plant
title_short A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power Plant
title_full A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power Plant
title_fullStr A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power Plant
title_full_unstemmed A Process for Evaluating Adverse Environmental Impacts by Cooling-Water System Entrainment at a California Power Plant
title_sort process for evaluating adverse environmental impacts by cooling-water system entrainment at a california power plant
publisher Hindawi Limited
series The Scientific World Journal
issn 1537-744X
publishDate 2002-01-01
description A study to determine the effects of entrainment by the Diablo Canyon Power Plant (DCPP) was conducted between 1996 and 1999 as required under Section 316(b) of the Clean Water Act. The goal of this study was to present the U.S. Environmental Protection Agency (EPA) and Central Coast Regional Water Quality Control Board (CCRWQCB) with results that could be used to determine if any adverse environmental impacts (AEIs) were caused by the operation of the plant’s cooling-water intake structure (CWIS). To this end we chose, under guidance of the CCRWQCB and their entrainment technical working group, a unique approach combining three different models for estimating power plant effects: fecundity hindcasting (FH), adult equivalent loss (AEL), and the empirical transport model (ETM). Comparisons of the results from these three approaches provided us a relative measure of confidence in our estimates of effects. A total of 14 target larval fish taxa were assessed as part of the DCPP 316(b). Example results are presented here for the kelp, gopher, and black-and-yellow (KGB) rockfish complex and clinid kelpfish. Estimates of larval entrainment losses for KGB rockfish were in close agreement (FH is approximately equals to 550 adult females per year, AEL is approximately equals to 1,000 adults [male and female] per year, and ETM = larval mortality as high as 5% which could be interpreted as ca. 2,600 1 kg adult fish). The similar results from the three models provided confidence in the estimated effects for this group. Due to lack of life history information needed to parameterize the FH and AEL models, effects on clinid kelpfish could only be assessed using the ETM model. Results from this model plus ancillary information about local populations of adult kelpfish suggest that the CWIS might be causing an AEI in the vicinity of DCPP.
url http://dx.doi.org/10.1100/tsw.2002.182
work_keys_str_mv AT cpehrler aprocessforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT jrsteinbeck aprocessforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT ealaman aprocessforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT jbhedgepeth aprocessforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT jrskalski aprocessforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT dlmayer aprocessforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT cpehrler processforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT jrsteinbeck processforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT ealaman processforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT jbhedgepeth processforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT jrskalski processforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
AT dlmayer processforevaluatingadverseenvironmentalimpactsbycoolingwatersystementrainmentatacaliforniapowerplant
_version_ 1725324515776397312