IEPA ATTACHMENT NO.

Center for Applied Bioassessment 6z Biocriteria

P.O. Box 21541

Columbus, OH 43221.0541

Temperature Criteria Options for the

Lower Des Plaines River

Final Report

to

U.S. EPA, Region V

Water Division

77 W. Jackson Blvd

Chicago, IL 60605

and

Illinois EPA

Bureau of Water

1021 North Grand Avenue East

P.O. Box 19276

Springfield, Illinois 62794-9276

Des:Plaines R. '

below Dresden Dam (Hey & Assoc. 2003)

October 11, 2005

Chris 0. Yoder, Research Director

Midwest Biodiversity Institute

P.O. Box 215641

Columbus, OH 43221-0561

and

Edward T. Rankin, Senior Research Associate

Center for Applied Bioassessment and Biocriteria

P.O. Box 21541

Columbus, OH 43221-0541

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October

11, 2005

Introduction

The Center for Applied Bioassessment and Biocriteria (CABB) was requested by U.S. EPA,

Region V and the Illinois EPA to develop temperature criteria options for the Lower Des

Plaines River in northeastern Illinois. The need to review and possibly revise the existing

temperature criteria is a result of the recent use attainability analysis (UAA) conducted for

the Brandon and Dresden navigation pools of the mainstem (Hey and Associates 2003).

CABB produced a draft report in June 2004 on temperature criteria options for three

different use designation scenarios based on the outcomes of the UAA process. Since that

time, the methodology used to derive seasonal temperature criteria options (Ohio EPA

1978) was updated (MBI 2005), thus the June 2004 draft report is revised herein. The

revised methodology emanates from that originally developed by Ohio EPA (1978) and

later described by Yoder and Emery (2004). A project to review the temperature criteria for

the Ohio River was the impetus for these revisions

.

and included an examination of

existing temperature criteria models and techniques, a review of state temperature criteria

and methods, and an extensive update to the thermal tolerance database for freshwater

fishes common to rivers and streams of the Great Lakes and Ohio River drainages. The

new data and methodologies developed by this effort were used in this revision of the

Lower Des Plaines temperature criteria options report.

Project Background

The Brandon and Dresden navigation pools of the Lower Des Plaines River were the

subject of a use attainability analysis (UAA) conducted by Hey and Associates (2003). The

purpose of the UAA was to evaluate the efficacy of the existing Secondary Contact/

Indigenous Aquatic Life use designation and the potential for upgrading to the General

use designation or an intermediate designation that reflects the modified habitats of these

navigation pools and impoundments. Regardless of the use designation decision that is

ultimately made by Illinois EPA, the current temperature criteria for the Lower Des Plaines

River could be changed. Thus, Illinois EPA is interested in developing options for

temperature criteria that more closely reflect the potential biological assemblages that are

representative of the possible designated use outcomes of the UAA process.

Project Purpose

The primary purpose of this report is to develop options for ambient temperature criteria

for the Lower Des Plaines River within the objectives of the directives for this project. The

temperature criteria options are the result of several variables and assumptions the most

important of which are the lists of representative aquatic species (RAS) and the statistical

endpoints used to analyze the ambient temperature database. Multiple RAS lists were

developed and varied by use designation option and the inclusion and exclusion of key fish

species within each. Ambient temperature data collected in the Lower Des Plaines R. and

the Chicago Area Waterway System (CAWS) was analyzed and statistical thresholds were

developed for later use in selecting non-summer season criteria. The results of a thermo-

dynamic modeling study of this area (Holly and Bradley 1995) were also used to calculate

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

ambient temperatures. From these options, Illinois EPA should be able tO derive a set of

seasonal temperature criteria to apply to the Des Plaines R. and in consideration of the use

designation options emanating from the UAA process.

It is not the purpose of this report to make these determinations. Neither is it the purpose

of this report to determine or allocate heat loads for specific sources based on the ambient

temperature criteria options. Presently, deriving temperature criteria is a separate function

apart from applying them to specific water pollution control issues such as NPDES permits

or TMDLs. One of the most difficult issues in setting temperature criteria is the

consideration of "normal" ambient thermal regimes and naturally occurring exceedences of

fixed seasonal criteria. It is possible and perhaps likely that thermal thresholds for key RAS

will be exceeded on occasion by natural thermal regimes, thus triggering criteria

exceedences and their potential consequences. Such exceedences are of particular concern

where they are frequent enough to result in the perception of an impaired designated use.

However, as with other naturally occurring physical and chemical constituents, exceedences

are inevitable and may not necessarily result in a biologically impaired use (Essig 1998).

Conversely, setting criteria too high to avoid the regulatory inconveniences of such

exceedences can have potentially adverse biological consequences. These issues must be

considered when deriving and applying temperature criteria.

Objectives, Approach, and Methods

The principal objective of this project is the development of seasonal temperature criteria

options that are protective of the biological assemblages that are representative of the

designated use options that may be considered for the Lower Des Plaines River. Using the

same approach as the recently completed Ohio River methodology (MBI 2005), these were

derived based on the representative fish assemblages for each designated use option. The

methodology uses data from the thermal effects literature to create a thermal effects

database for freshwater fish. This data is then used within a procedure that calculates four

behavioral and physiological thresholds for a list of representative fish species termed RAS

(Representative Aquatic Species) that are intended to represent the fish assemblage of a

particular river or river segment. Ohio EPA used this approach in setting temperature

criteria for inland waters and Lake Erie in the 1978 revisions to the Ohio water quality

standards (WQS) and ORSANCO used it to adopt the current Ohio River temperature

criteria in 1984. The temperature criteria derivation process was later incorporated within

the Fish Temperature Modeling system that is part of the Ohio ECOS data management

system developed and operated by Ohio EPA. The Fish Temperature Modeling system was

originally developed as a mainframe routine, but was later converted to a relational

database (FoxPro) as part of the Ohio ECOS data management system. MBI developed an

update to this system as part of the Ohio River thermal criteria update (MBI 2005). It

operates in an Excel format using Visual Basic - this system was used to develop the

current set of temperature criteria options for the Lower Des Plaines R.

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

Comprehensive Literature Search and Compilation of Recent Fish Thermal-effects Data

The original Ohio EPA (1978) methodology used thermal effects data from 370+ literature

sources that date before 1978. One of the major tasks of the ORSANCO sponsored study

(MBI 2005) was to update the thermal effects database by obtaining new literature sources.

A database search focused on keywords related to thermal effects on fish and other aquatic

organisms. More than 500 titles and abstracts were screened for relevancy. In addition,

other new literature sources not revealed by the database search were obtained via reviews

of individual publications, major bibliographies, web links, and "word of mouth". In all,

this effort produced more than 200 new and

useable

references that included specific

thermal effects data for individual species or groups of fishes and invertebrates:- An

additional 200+ sources were reviewed, but deemed unsuitable for these purposes. An

attempt was made to obtain thermal effects data for other assemblage groups such as

bivalve mollusks, but there was very little if any usable information that could be found.

The MBI (2005) compilation emphasized freshwater fishes of the Ohio River and Great

Lakes drainages, but also included a compilation for selected macroinvertebrates.

Each new literature source was reviewed for relevancy, i.e., were the specific thermal

tolerance endpoints used in the Fish Temperature Model readily available? Acceptable

data were then entered into the master thermal effects database. The original literature

source was examined for relevancy, originality, and completeness as much as was possible

prior to accepting the data in the master database. The acceptance of "extrapolated" (i.e.,

without a direct review of the original publication) citations was done for some of the more

comprehensive thermal effects compendia such as Brown (1974),Wismer and Christie

(1987), Hokanson (1990), and Beitinger et al. (2000). A notation was made about the

extrapolated citation of such references. We did find in some of these compendia a

practice of citing an existing literature review as the source of the data in lieu of the

original literature source. We avoided duplicating this practice and where it occurred we

cited the original literature source.

Thermal Endpoints

The compilation originally produced by Ohio EPA (1978) relied mostly on the upper

incipient lethal temperature (UILT) as the primary lethal endpoint. It is the principal basis

for calculating the short and long term survival thresholds produced by the Fish

Temperature Model. The UILT was the accepted lethal endpoint of that time (Brown

1974). The other widely available test endpoint, the critical thermal maximum (CTM), was

thought to produce lethal temperatures that were too high to be protective in nature

because the test organisms are not properly acclimated by the rapid increases in test

temperatures. As such, the CTM endpoint occurs beyond the temperature at which the

organism is irreparably harmed. A long standing concern with all of the commonly

available lethal test methods is that the steady or regular increases in test temperature

inherent to the methodologies do not reflect environmental reality. This concept is amply

illustrated by Figure 1 (from Bevelheimer and Bennet 2000) in which the accumulation of

thermal stress to an aquatic organism is dependent on seasonal acclimation, the severity

and duration of periods of thermal exposure and stress, and the duration of recovery

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Thcrmatstrossas

24

22

Q

v.20

16

7,1

Seasonal

—acclimation

1

811?

tats

?

8/31

CABB/MBI

Lower Des Plaines Temperature Criteria Options October 11, 2005

periods, i.e., lower temperatures that are closer to physiological optima. Unfortunately,

few if any of the available

in situ

tests reflect this type of thermal exposure. Field derived

thresholds (final preferenda and upper avoidance) better represent these phenomena, but

only if a full range of thermal exposures was reasonably available in the study area.

Figure 1. The important

features of

the thermal

regime

that is important in determining the

effects of

temperature on fish (after Bevelheimer and Bennet 2000).

While thermal resistance seems to increase with slowly increasing temperatures, does it

represent reality in the environment where temperatures fluctuate up and down within a

season? The few studies that have attempted to examine the effect of fluctuating test

temperatures have produced conflicting results. Unfortunately, insufficient experimental

data exists to support what might be viewed as "real time" temperature criteria in lieu of

the current technology of fixed seasonal criteria. As one result, safety factors are commonly

employed in interpreting thermal effects endpoints and in deriving temperature criteria.

The choice (or order of preference) of thermal endpoints was an important issue in the

MBI (2005) update study. Clearly, different testing procedures can and do produce

different thermal endpoints for the same species. The key technical issue with the

traditional upper thermal tolerance testing procedures (CTM and UILT) is not the

procedures themselves, but their disconnection with natural exposure regimes (see Figure

1). Selong et al. (2001) summarized the limitations of upper thermal endpoint data using

these two methods:

"However, their [CTM test results] relevance to the actual temperature

tolerance of fishes is limited by the unnaturally rapid temperature changes,

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CABB/MBI

Lower Des Plaines Temperature Criteria Options October

11, 2005

which preclude the normal acclimation that occurs in nature . . . However, as

with the CTM method, the ILT method may have limitations when it comes to

extrapolating test results to natural situations. A recent modification of the ILT

method incorporates slower temperature change schedules (e.g., 1.0-1.5°C/d)

to better mimic natural temperature changes and reduce (unnatural) thermal

shock (Smith and Fausch 1997). However, another potential limitation of the

ILT method still remains, as temperature tests are typically run for a short

duration (<7 days; Elliott and Elliott 1995) and the effects of longer exposures

are often unknown. (p. 1027)."

The authors tested the short-term and chronic effects of elevated temperature on bull

trout using the acclimated chronic exposure (ACE) method, which is a modification of

the CTM and ILT procedures. This method entails gradually adjusting water

temperatures at environmentally realistic rates that allow fish to fully acclimate to

changing conditions (e.g., 1.0-1.5°C/day). Hokanson and Koenst (1986) further

described the "slow heating" method to define chronic thresholds. More recently

Reash et.al. (2000) derived upper thermal tolerance data for smallmouth and golden

redhorse using this method. However, comparatively few studies based on this new

method exist and it does not address the phenomena portrayed by Figure 1. Some of

the studies included in the MBI (2005) update were conducted under rising and falling

ambient temperatures, but the results were mixed in terms of whether it changed the

eventual thermal endpoints.

When upper thermal endpoints were available for more than one method the MBI

(2005) study selected lethal endpoints based on the following (most preferred listed

first):

1.

"slow heating" method (e.g., a method analogous to ACE) that we term here the

chronic thermal maximum (ChTM);

2.

upper incipient lethal temperature (UILT) at acclimation temperatures of 25-30°C;

3.

critical thermal maximum (CTM) based on the fast heating method (0.5-1.0°C/hr.)

with appropriate adjustments (i.e., safety factors) to account for the inherent over-

estimation of lethality.

Very few slow heating (ChTM) method test results were found by MBI (2005). In fact,

much of the new literature included the least preferred CTM based on the fast heating

method. The papers that described the slow heating method agreed that slowly increasing

test temperature followed by daily cooling was "probably the most environmentally realistic

exposure regime". However, the availability of test results using this approach is virtually

non-existent. The practical impact to this and similar studies is a continued need to rely

on the UILT and the use of additional safety factors for the conversion of CTM results.

Methodology

Four thermal input variables are used in the Fish Temperature Model to determine the

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October

11, 2005

summer (June 16-September 15) average and daily maximum temperature criteria.

However, in developing the baseline input variables, up to six thermal parameters were first

considered by Ohio EPA (1978) and this was followed by MBI (2005). General concepts of

thermal responsiveness (e.g., acclimation) were considered and are discussed in more detail

in MBI (2005). Of the six thermal parameters that were inventoried for each fish species,

the upper incipient lethal temperature (UILT), chronic thermal maximum (ChTM), and

the critical thermal maximum (CTM) are considered lethal thresholds and the remaining

four (optimum, final preferendum, growth, and upper avoidance) are considered sublethal

thresholds. At the time the Ohio EPA methodology was developed, the rapid transfer

methad_(from

which the UILT-is derived) was viewed as providing a preferred basis for

physiological response than did the fast heating method on which the CTM is based.

Each of the six thermal parameters are defined as follows:

Upper Incipient Lethal Temperature - at a given acclimation temperature this is the

maximum temperature beyond which an organism cannot survive for an indefinite

period of time;

Chronic Thermal Maximum - the temperature at which a test organism dies resulting from

a slow and steady increase in temperature (<1.0-1.5°C/day); this newly developed

endpoint is representative of the upper lethal temperature that can be tolerated

indefinitely.

Critical

Thermal Maximum - the temperature at which a test organism experiences

equilibrium loss resulting from a rapid and steady increase in temperature (>0.5-1.0

°C/hr.);

Optimum - the temperature at which an organism can most efficiently perform a

specific physiological or ecological function;

Final Preferendum -

the temperature at which a fish population will ultimately

congregate regardless of previous thermal experience (Fry 1947);

Upper Avoidance

Temperature - a sharply defined upper temperature at which an organism

at a given acclimation temperature will avoid (Coutant 1977);

Growth - the Mean Weekly Average Temperature (MWAT) for growth (Brungs and Jones

1976). The MWAT can be calculated if a minimum of three of the six thermal parameters

is available.

Data garnered from the comprehensive review of the thermal effects literature were

characterized as one or more of the preceding thermal endpoints in the compilation of

temperature effects database (MBI 2005).

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

Fish Temperature Model

The Fish Temperature Model uses four thermal input parameters that include: 1) the

optimum or final preferendum; 2) the mean weekly average temperature (MWAT) for

growth; 3) the upper avoidance temperature; and, 4) the upper lethal temperature at

acclimation temperatures of 25-30°C. Thermal parameters compiled by MBI (2005) were

used as the primary database for deriving the Lower Des Plaines R. temperature criteria

options (see Appendix A). The four primary thermal parameters are stored by species and

accessed by the model when a species is designated as an RAS for a particular designated

use/RAS option. Different values could also be substituted to determine the effect of

thermal tolerance values on the resulting temperature criteria calculations. However, the

substitute thermal endpoints must first meet the criteria for inclusion in the thermal effects

database (MBI 2005).

Representative Aquatic Species (RAS)

The derivation of a given temperature criteria option is dependent on the development

of a list of representative aquatic species (RAS), which is one of the primary input

variables for the model. Because thermal effects data are not available for all species in

an assemblage, the list of RAS constitute a subset of the potential assemblage being

comprised of species that have sufficient thermal tolerance data from which temperature

criteria can be derived. Thus an inherent assumption of this process is that all of the

species not included as RAS will be protected by extension. This assumption is valid so

long as there is adequate representation of thermally sensitive species. The recently

completed update to the thermal database (MBI 2005) increased the representation of

these species.

Species that are generally regarded as being highly to moderately tolerant to a variety of

environmental impacts tended to be over-represented in these databases, which is a

common occurrence in databases for many water quality parameters. Tolerant species

were more accessible and were more easily handled in laboratory tests, hence their

predominance in these databases. In our compilation, these species were the most

frequently studied and usually had data available for all six of the thermal thresholds

previously described. Conversely, the data for species regarded as highly or moderately

intolerant tended to be available for fewer thermal thresholds and were oftentimes based

largely on field studies. As such, and until these species are tested more frequently, there

remains a significant risk that the most sensitive groups of species will not be adequately

protected. Our approach is simply a best attempt to represent the entirety of the potential

assemblage and it is naturally limited by the extant thermal tolerance database. As such,

the model output will propagate a degree of uncertainty, which can be considered in the

eventual derivation and application of the temperature criteria.

In developing a list of representative fish species for a particular water body or segment,

the following criteria for membership were used:

• species that represent the full range of response and sensitivity to environmental

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

stressors;

•

species that are commercially and/or recreationally important;

•

species that are representative of the different trophic levels;

•

rare, threatened, endangered, and special status species;

•

species that are numerically abundant or prominent in the system;

•

potential nuisance species; and,

•

species that are indicative of the ecological and physiological requirements of

representative species that lack thermal data.

The historical occurrence of fish species in a particular water body is an important

consideration in the development of an RAS list, particularly in historically degraded

waters. These criteria were followed in developing the RAS lists for the Lower Des Plaines

River for each of the three designated use options that are under consideration via the

UAA process. The resulting selections reflect the species membership expectations for the

fish assemblage that would be expected to occur within each designated

.

use option (Table

1). The General Use is expected to support a diverse, warmwater fish assemblage that is

expected to occur in the least disturbed, free-flowing habitats of the Lower Des Plaines

mainstem and similarly sized rivers in the region. The Modified Use option is intended to

apply to physically modified riverine habitats characteristic of the areas that are inundated

by artificial impoundment by low head dams. The Secondary Contact/Indigenous Aquatic

Life use option is represented by an assemblage that is tolerant of the most extreme

physical and hydrological modifications (gross habitat loss and simplification). As such,

each designated use option ranging from General to Secondary Contact represents a

progressive loss of the species that are incompatible with the increasing physical and

hydrological modifications that are characteristic of each designated use option. Data

compiled in Hey & Associates (2003) and Smith (1979) were the principal sources used to

compile the RAS lists. The RAS lists have increased in terms of species membership since

the 2004 draft of this report due primarily to the addition of thermal tolerance data for

new species by MBI (2005). Based on the MBI study, thermal tolerance data for 35 new

species in addition to the 62 species originally compiled by Ohio EPA (1978) was included.

Hence the addition of new species has increased the number of RAS in this study.

Derivation of Seasonal Temperature Criteria Options

The principal objective of this project is the development of seasonal temperature criteria

options for the range of possible outcomes of the UAA process. These include thermal

requirements for:

1)

a warmwater habitat assemblage that is consistent with the Illinois General Use;

2)

an assemblage that reflects the habitat modified conditions of the impounded

portions of the Lower Des Plaines River (Modified

Use); and,

3)

an assemblage that represents significantly limited conditions that approximate the

Illinois Secondary Contact/Indigenous Aquatic Life use.

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

Table 1. Representative fish species used to derive temperature criteria for the Lower Des

Plaines River for three designated use options.

Membership

?

General Modified Secondary

Species

?

Rationale

?

Use

?

Use

?

Contact

Longnose gar

(Lepisosteus osseus)

Skipjack herring (Alosa chrysoch/oris)

Gizzard shad (Dorosoma cepedianum)

Northern pike (Esox Lucius)

Bigmouth buffalo (Ictiobus cyprinella)

Smallmouth buffalo-

(I.

niger)

Quillback (Carpiodes cyprinus)

River carpsucker (C. carpio)

Golden redhorse (Moxostoma erythrurum )

Golden redhorse (Moxostoma erythrurum )

Smallmouth redhorse (M. breviceps)4

Northern hog sucker (Hypentelium

nigricans)

White sucker (Catostomus commersonii)

Common carp (Cyprinus carpio)

Golden shiner (Notemigonus

crysoleucas)

Creek chub (Semotilus atromaculatus)

Emerald shiner (Notropis atherinoides)

Redfin shiner (Lythrurus umbratilis)

Striped shiner (Luxilis chrysocephalus)

Spottail shiner (Notropis hudsonius)

Spotfin shiner (Cyprinella spiloptera)

Bigmouth shiner (Notropis

dorsalis)

Sand shiner (Notropis stramineus)

Fathead minnow (Pimephales

promelas)

Blunmose minnow

(Pimephales

notatus)

Stoneroller (Campostoma anomalum)

Channel catfish (Ictalurus punctatus)

Yellow bullhead (Ameirus natalis)

Black bullhead (Ameirus melas)

Flathead catfish (Pylodictis olivaris)

Stonecat madtom (Noturus flavus)

Blackstripe topminnow (Fundulus notatus)

Brook silversides (Labidesthes

sicculus)

White bass (Morone

chrysops)

White crappie (Pomoxis annularis)

Historical'; 1994-20022

1994-2002

Historical; 1994-2002

?

X

Kankakee R.

1994-2002

1994-2002

1994-2002

1994-2002

Historical; 1994-2002

Silver redhorse3; 1994-2002

Historical; 1994-2002

Historical

Historical

Historical; 1994-2002

?

X

Historical; 1994-2002

?

X

Historical

Historical; 1994-2002

Historical

Historical; 1994-2002

1994-2002

Historical; 1994-2002

Historical

Historical

Historical

?

X

Historical; 1994-2002

Historical

1994-2002

Historical

Historical

X

1994-2002

Historical

1994-2002

1994-2002

Historical

Historical; 1994-2002

Historical occurrence reported in Smith (1979).

= Species collected in the UAA study segment between 1994-2002.

3

Silver

redhorse retained in the modified use option - golden redhorse data used as a surrogate.

Smallmouth redhorse used as surrogate for shorthead redhorse.

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Table 1. continued.

Membership

?

General Modified Secondary

Species

?

Rationale

?

Use?

Use

?

Contact

Black crappie (P.

nigromaculatus)

Rock bass (Ambloplites

rupestris)

Smallmouth bass (Micropterus dolomieui)

Largemouth bass (M.

salmoides)

Green sunfish (Lepomis cyanellus)

Bluegill sunfish (L. macrochirus)

Orangespotted sunfish (L. humilis)

Longear sunfish (L. megalotis)

Pumpkinseed sunfish (L. gibbosus)

Walleye (Sander vitreus)

Sauger (Sander

canadense)

Dusky darter (Percina sciera)

Johnny darter (Etheostoma nigrum)

Fantail darter

(Etheostoma

flabellare)

Freshwater drum (Aplodonitus grunniens)

Total RAS

Historical; 1994-2002

Historical; 1994-2002

Historical; 1994-2002

Historical; 1994-2002

Historical; 1994-2002

Historical; 1994-2002

1994-2002?

•

1994-2002

Historical; 1994-2002

Kankakee

Kankakee

Blackside5

; Hist.; '94-'02

Historical

Historical

Historical; 1994-2002

X

X?

X

X

X

X

X

X?

X

49?

27

X

X

8

This does not presuppose the application of these designated use options via the UAA

process, but rather represents options reflecting the range of restoration possibilities and

limitations for the Lower Des Plaines River.

Summer Temperature

Criteria

The summer months represent the most stressful period for fish in terms of exposure to

high temperatures. However, this should not be construed as the only season in which

adverse effects can occur, thus other effects during the non-summer seasons are also

considered in the derivation of seasonal criteria. For the purposes of temperature criteria

development and application, the summer period is June 16 - September 15.

The Fish Temperature Model calculates average and daily maximum summer temperature

criteria via an analytical process based on that originally developed by Bush et al. (1974).

The calculation software of the model was recently revised and it produces these values

using the database and thermal parameters compiled by MBI (2005). Temperature

tolerance values for 97 fish species considered representative of the Ohio River and Great

Lakes drainages are presently contained in the model's database. These values include the

four primary thermal parameters described previously (optimum, mean weekly average for

5

Dusky darter used as a surrogate for blackside darter.

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Lower Des Plaines Temperature Criteria Options October 11, 2005

growth, upper avoidance, and upper incipient lethal temperatures). The model permits

alternative thermal values to be substituted, thus the effect of species-specific differences on

the derivation of summer season thresholds can be evaluated - these can be maintained as

alternate databases. The procedure is simply one of listing each representative species

under each thermal parameter adjacent to the whole Fahrenheit temperature when it is

exceeded. The cumulative effect of increasing temperature is readily apparent as additional

species thermal criteria are exceeded. This process indicates where the various species

occur (with respect to temperature) relative to each other and does not indicate exact

thresholds or limits. The temperatures at which 100%, 90%, 75% and 50% of the

representative species four primary thermal thresholds (optimum, growth, upper

avoidance, and UILT) are exceeded are determined to show what proportion of the

representative assemblage is protected at a given temperature. The long-term survival

temperature is calculated from the short-term survival temperature (i.e., the UILT) as UILT

- 2°C. The tolerance values in the existing model were initially used in the derivation of

the summer average and maximum temperature criteria for the different designated use

options being considered for the Lower Des Plaines River.

Derivation of Seasonal Temperature Criteria

The derivation of seasonal temperature criteria for each of the designated use options

considered in this analysis included summer season average and maximum values based on

the output of the Fish Temperature Model. Non-summer season criteria included

consideration of species-specific spawning thresholds (MBI 2005) and consistency with the

historical ambient temperature record, which in this case is based on analyses of long-term

temperature monitoring data in the Lower Des Plaines R. and Chicago Area Waterway

System (CAWS) upstream from the Brandon Pool and outside the direct influence of

other sources of heat (Appendix B). In keeping with the guidance of Ohio EPA (1978) and

MBI (2005), we adhered to the following in deriving the temperature criteria options:

Averages should be consistent with:

1) 100% long-term survival of all representative fish species;

2)

growth of commercially or recreationally important fish species;

3)

growth of at least 50% of the non-game fish species;

4) 100% long-term survival of all endangered fish species; and

5)

the observed historical ambient temperature record.

Daily maxima should be consistent with:

1)

100% short-term survival of all representative fish species; and

2) the observed historical ambient temperature record.

Summer Average and Maximum Criteria

Summer average and maximum temperature criteria were calculated in accordance with the

outputs of the Fish Temperature Model. These apply during the defined summer period

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of June 16 - September 15 as daily maxima and as a period average. The rationale for a

period average as opposed to a daily, weekly, or monthly average is in recognition of the

realities of within season temperature variations and the thermal tolerances of fish.

Neither is a "smooth" function as within season changes include naturally occurring

temperatures that can approach or exceed thermal tolerances and which fall below these

thresholds. It also includes the knowledge that fish can avoid or withstand occasional

exceedences of the short-term survival thresholds, provided that local refuges are available

and/or the duration of these periods are sufficiently brief (see Figure

1). Meeting the long-

term period average requires equivalent "cool down" periods when temperatures are well

below the survival thresholds and closer to the physiological thresholds for growth and

maintenance (see Figure 1).

The results of the Fish Temperature Model outputs for the three designated use options

are portrayed in Tables 2 and 3 (summer season only) and Appendix A (primary model

outputs). These were derived by using the RAS lists for each designated use option (Table

1) as the major input variables.

General

Use

The original general use RAS list in the 2004 draft report included thirty (30) fish species.

With the additional thermal data provided in MBI (2005), the general use RAS list now

includes 49 fish species. We added two additional variations to the General Use RAS list -

one adding yellow perch, walleye, and sauger and another removing stonecat madtom from

the original RAS list. These changes were made to determine the sensitivity of adding and

removing key RAS. The results are summarized in Table 2 and the long term and short

term survival thresholds that protect 100% of the RAS represent summer average and

maximum criteria options for the period June 16 - September 15. For the updated

General Use RAS list a summer period average temperature of 27.0°C (80.6°F) and a daily

maximum of 29.0°C (84.2°F) will protect for the long term survival of 100% of the RAS.

The period average of 27.0°C exceeds the upper avoidance temperature of one RAS

(stonecat madtom) by 1.3°C. Thirteen (13) RAS are considered to be either commercially

or recreationally important - the 27.0°C period average exceeds the growth temperature for

one of these species (northern pike) by 1.7°C. No Illinois rare, threatened, or endangered

species are among the species included in any of the RAS lists. The revised criteria based

on the updated RAS list (compared to the 2004 original draft list) are 0.5°C lower. We

also tested the influence of species additions by adding yellow perch, sauger, and walleye.

While these species were not included by the review of historical distribution data and

occurred in very low numbers in the 1994-2002 databases, each occurs in the Kankakee

River or the CAWS and they are expected to occur in the Lower Des Plaines R. as water

quality conditions improve in the near future. The inclusion of these species did not

change the model outputs, thus the aforementioned criteria should be protective of these

species. However, the growth criteria of sauger and walleye are exceeded by the period

average of 27.0°C by 0.1°C and 0.8°C, respectively. Stonecat madtom was the most

thermally sensitive species in the updated RAS list. Removing this species changed the

period average to 29.5°C and the daily maximum to 31.5°C. This option exceeded the

12

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CABB/MBI

Lower Des Plaines Temperature Criteria Options October

11,

2005

Table 2. Fish temperature model outputs (°F[°C]) for four RAS variations of the Illinois

General Aquatic Life use designation for the Lower Des Plaines River. The long-term

and short-term survival temperatures represent summer season (June 16 - September

15) average and maxima.

-Thermal

Category

Proportion of Representative Fish Species

100%

90% 75%

50%

General Use Original RAS

(2004 draft)

Optimum

72.5

(22.5)

77

.

7

(25.4)

81.1

(27.3)

83.1

(28.4)

Growth (MWAT)

78.3

(25.7)

82.4

(28.0)

84.7 (29.3)

86.9 (30.5)

Avoidance (UAT)

83.3

(28.5)

85.1

(29.5)

87.3

(30.7)

88.9

(31.6)

Survival (Long-term)

85.1

(29.5)

86.9 (30.5)

88.5

(31.4)

91.2

(32.9)

Survival (Short-term)

88.7 (31.5)

90.5 (32.5)

92.1 (33.4)

94.8

(34.9)

General Use RAS

I

(expanded

list 2005)

Optimum

67.4

(19.7)

72.7

(22.6)

81.1 (27.3)

82.8 (28.2)

Growth

(MWAT)

74.8 (23.8)

79.1

(26.2)

84.6 (29.2)

86.7

(30.4)

Avoidance (UAT)

78.3

(25.7)

84.7 (29.3)

87.3 (30.7)

88.9 (31.6)

Survival (Long-term)

80.6

(27.0)

86.9

(30.5)

88.7 (3L5)

90.9 (32.7)

Survival (Short-term)

84.2 (29.0)

90.5 (32.5)

92.3 (33.5)

94.5 (34.7)

General Use RAS

2

(adds yellow perch,

sauger,

and

walleye)

Optimum

67.4 (19.7) 72.7

(22.6)

78.3 (25.7)

82.6 (28.1)

Growth (MWAT)

74.8

(23.8)

78.8

(26.0)

82.8 (28.2)

86.5

(30.3)

Avoidance (UAT)

78.3 (25.7)

85.1 (29.5)

86.9 (30.5)

88.9 (31.6)

Survival (Long-term)

80.6 (27.0)

86.9 (30.5)

88.3 (31.3)

90.9 (32.7)

Survival (Short-term)

84.2 (29.0)

90.5 (32.5)

91.9

(33.3)

94.5

(34.7)

General Use RAS

3 (removes stonecat

madtom from RAS

2)

Optimum

67.4

(19.7)

72.9

(22.7)

78.8 (26.0)

82.6

(28.1)

Growth (MWAT)

75.4 (24.1)

79.2 (26.2)

82.9

(28.3)

86.5 (30.3)

Avoidance (UAT)

83.3 (28.5)

85.5 (29.7)

87.1

(30.6)

88.9 (31.6)

Survival (Long-term)

85.1

(29.5)

87.3 (30.7)

88.5 (31.4)

90.9 (32.7)

Survival (Short-term)

88.7

(31.5)

90.9 (32.7)

92.1

(33.4)

94.5

(34.7)

UAT of fifteen (15) RAS and the growth criterion of four (4) recreational and

commercially important species.

13

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CABB/MBI

Lower Des Plaines Temperature Criteria Options October

11, 2005

Table 3. Fish temperature model outputs (°F[°C1) for fish species representative of a

modified use (two versions) and the Secondary Contact/Indigenous Aquatic Life use

for the Lower Des Plaines River. The long-term and short-term survival temperatures

represent summer season (June 16 - September 15) average and maxima.

Thermal

Proportion of Representative Fish Species

Category

100% 90% 75% 50%

Modified Use RAS 1 (includes golden redhorse)

Optimum

71.2

(21.8)

75.4 (24.1)

81.3

(27.4)

82.6

(28.1)

Growth (MWAT)

77.5

(25.3)

81.0 (27.2)

85.8

(29.9)

86.7

(30.4)

Avoidance (UAT)

83.7 (28.7)

•

84.9

(29.4)

87.1

(30.6)

88.9 (31.6)

Survival

(Long-term)

85.1 (29.5)

86.5 (30.3)

89.1 (31.7)

91.4

(33.0)

Survival (Short-term)

88.7

(31.5)

90.1 (32.3)

92.7

(33.7)

95.0 (35.0)

Modified Use RAS 2 (excludes golden redhorse)

Optimum

71.2

(21.8)

75.0 (23.9)

81.5 (27.5)

82.8

(28.2)

Growth (MWAT)

77.5

(25.3)

80.6

(27.0)

85.8

(29.9)

86.9 (30.5)

Avoidance (UAT)

83.7

(28.7)

85.6 (29.8)

87.4 (30.8)

89.1

(31.7)

Survival (Long-term)

85.1 (29.5)

86.5 (30.3)

89.8

(32.1)

91.4

(33.0)

Survival (Short-term)

88.7

(31.5)

90.1

(32.3)

93.4 (34.1)

95.0

(35.0)

Secondary Contact/Indigenous Aquatic Life

Optimum

81.0

(27.2)

81.1

(27.3)

82.4

(28.0)

84.1

(29.0)

Growth (MWAT)

85.3 (29.6)

85.4

(29.7)

86.7

(30.4)

87.7

(31.0)

Avoidance (UAT)

87.8 (31.0)

87.8

(31.0)

88.0 (31.1)

91.9

(33.3)

Survival (Long-term)

88.3 (31.3)

88.6

(31.4)

90.5

(32.5)

93.0 (33.9)

Survival (Short-term)

91.9

(33.3)

92.2

(33.4)

94.2

(34.5)

96.6

(35.9)

Modified Use

Twenty-seven (27) fish species are considered representative of the intent of a theorized

Modified Use, which reflects the irretrievable habitat modifications caused by

impoundments formed by low head dams. The deletion of 22 species from the General

use list reflects the biological consequences of the inundation of run and riffle habitats by

the resulting impoundment. Two scenarios were developed for this designated use option;

one including silver redhorse and the other excluding this species. Of the redhorse species

that are potential inhabitants of the Lower Des Plaines River system, silver redhorse would

likely tolerate impounded conditions. To calculate the temperature criteria, golden

redhorse was used as an RAS surrogate since the thermal tolerance data are presently

insufficient for silver redhorse (Ohio EPA 1978; MBI 2005). The results including silver

redhorse are a period average temperature of 29.5°C and a daily maximum of 31.5°C to

protect 100% of the modified habitat RAS during the summer period. The period average

14

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

of 29.5°C exceeds the upper avoidance temperature for three RAS and the growth

temperature for two of the recreationally important RAS. If silver redhorse are excluded,

there is no effect on the period average or maximum. The same period average of 29.5°C

exceeds the upper avoidance temperature for two species and the growth temperature for

two of the recreationally important RAS. Fifteen (15) RAS are considered to be either

commercially or recreationally important. No rare, threatened, or endangered species are

among the RAS for this use option.

Secondary Contact/Indigenous Aquatic

Life

Eight (8) species were selected as being representative of the intent of this designated use

option. These species are regarded as highly tolerant to most forms of anthropogenic

impacts including thermal enrichment. The results indicate that an average temperature of

30.4°C and a daily maximum of

32.4°C

will protect 100% of the RAS during the summer

period. The period average of 30.4°C does not exceed the upper avoidance temperature of

any RAS or growth temperature of any recreationally or commercially important RAS for

this designated use option.

Seasonal Temperature Criteria

Seasonal average and daily maximum temperature criteria for the General Use RAS 1

option are provided as an example of deriving and displaying a seasonal temperature

criteria option (Table 4). The derivation of the summer period (June 16 - September 15)

average and maximum criteria were just described. Non-summer season criteria are

derived to maintain seasonal norms and cycles of increasing and decreasing temperatures.

Important physiological functions such as gamete development, spawning, and growth

should be assured since these are products of each species long term adaptation to natural

climatic and regional influences of which temperature is a controlling factor. Thermal

tolerance data for these physiological endpoints is comparatively limited being available for

only a few RAS.

Seasonal ambient temperature data was analyzed from eight locations in the Lower Des

Plaines River and the CAWS for the period 1998 through 2004 (Appendix B). Monthly

and semi-monthly mean, geometric mean, median, 98th,

95th

,

90th

, 75th

,

and percentile

values were calculated based on daily readings (Appendix B). Also included were the

maximum temperatures that occurred once, twice, and three times in each period and the

interquartile ranges of 1.5 and 2.5 times beyond the

75th percentile (the non-parametric

analogs of standard error and standard deviation). The monitoring location at Route 83 in

the Cal Sag channel was used as a "background" location in Table 4. We used the

geometric mean as the monthly and semi-monthly average and the

98th percentile as the

daily maximum. Other statistical thresholds could be used to set the non-summer criteria.

The 75th

percentile has been used previously as the average since this takes in account the

occurrence of warmer temperatures in single years. None of the values in Table 5 exceeded

the spawning criteria for any of the RAS options (MBI 2005) and all except one value in

July were below the summer average (1.6-5.8°F) and maximum (0.4-4.4°F) tolerance values

for the RAS options used in Table 4. The Route 83 location on the Chicago Sanitary and

15

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CABB/MBI

Lower Des Plaines Temperature Criteria Options October 11, 2005

Ship Canal exhibited higher ambient temperatures, presumably the result of enrichment by

thermal sources, thus reflecting higher seasonal temperatures that would exceed the

thermal tolerances of the RAS. Other monitoring locations exhibited more pronounced

effects of thermal enrichment, thus these were rejected as being representative of

"background" ambient conditions. Table 5 provides a comparison of the different RAS

and designated use options and with two different options for non-summer season ambient

temperatures, the Cal Sag Rt. 83 location and the results of modeling by the Iowa Institute

of Hydraulic Research (IIHR; Holly and Brady 1995). We interpreted monthly

temperatures from their Figure 4-10 which provides estimates of maximum daily

temperature distributions at the 1-55 bridge with no thermal enrichment.

The determination of temperatures that are representative of ambient or "background"

conditions for the upper Des Plaines River is complicated by the physically and thermally

• altered characteristics of the Upper Illinois Waterway System and the Chicago Area

Waterway System. In addition to choosing a representative monitoring location to serve as

a data source for determining this benchmark, the outputs of predictive modeling can also

be used for this purpose. It is important to understand here that our primary purpose is to

determine a representative background temperature, not determine the acceptability of

different thermal loading scenarios. The Holly and Brady (1995) thermal modeling studies

included simulations of the upper Des Plaines River temperature in the absence of thermal

enrichment by electric generating stations. The study simulated summer season maximum

temperatures at the 1-55 bridge (the current upper boundary of the General Use

designation) of 82-83°F with no thermal

sources, i.e.,

the conditions that could be expected in

the absence of any thermal enrichment by electric generating station discharges (Figure

4.10 in Holly and Brady 1995). The maximum 75th

percentile values were 75-76°F, which

is also consistent with our analysis of the Cal-Sag Rt. 83 temperature monitoring location.

The non-summer season simulations were also consistent with the ambient values at this

location, thus the temperature data should adequately represent the background or

ambient conditions for this system. While the Upper Illinois Waterway System represents

a complex mix of natural and human influenced hydrologic and thermal alterations, we are

focused here primarily on the determination of representative background conditions as a

baseline for evaluating the consequences of thermal alterations and the management of

thermal loadings.

17

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CABB/MBI

Lower Des Plaines Temperature Criteria Options October 11, 2005

Table 4. Seasonal average and daily maximum temperature criteria (°F) for the Illinois

general aquatic life use RAS 1 option. Summer period temperatures from the Rt. 83

Cal Sag site appear in brackets and are based on the geometric mean and the 98th

percentile values (Appendix B). Non-summer season temperatures in the CSSC at Rt.

83 are in parentheses for comparison to a thermally enriched segment.

Month- Dates

Average6

maximum'

'

January 1-31

38.4

(49.5) 46.6

(54.8)

February 1-28

41.7

(51.1)

51.7

(56.9)

March 1-31

47.0

(54.8) 57.3

(62.4)

April 1-15

54.0

(59.2) 59.9 (63.2)

April 16.30

57.3 (58.8) 67.7 (65.0)

May 1-15

63.7 (65.8) 71.6 (75.3)

May 16-31

65.1

(68.4)

71.2

(74.0)

June 1-15

69.8

(70.9) 77.8

(77.3)

June 16.30

80.6 [74.8] 84.2 179.8]

July 1-31

80.6 [79.0]

84.2

[84.7]

August 1-31

80.6 [78.4] 84.2 [83.8]

September 1-15

80.6 [76.2] 84.2 [81.5]

September 16-30

69.9

(74.4) 75.7

(81.0)

October 1-15

63.7

(69.8)

71.2 (76.0)

October 16-31

59.8 (66.9) 68.0 (75.0)

November 1-30

53.0 (61.3) 63.6 (70.7)

December 1-31

43.4 (53.9)

56.9 (63.5)

Consistent with seasonal temperature

measured at the Route 83 (Cal Sag)

monitoring location.

Consistent with spawning criteria for

all representative fish species in

March, April, May, and June.

Average and maximum provide for

short and long-term survival of 100%

of representative fish species; one

minor exceedence of ambient temp.

at the Route 83 (Cal Sag) location.

Consistent with seasonal temperature

measured at the Route 83 (Cal Sag)

monitoring location.

Basis for Criteria

6

Average temperature over the representative period - set at the 75 th percentile of the period of record based

on the Rt. 83 Cal Sag site.

Daily maximum temperature - set at the value exceeded 3 times during the period of record at the Rt. 83

Cal Sag site.

16

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

Table 5. Comparison of six temperature criteria options (average/maximum [°F]) for four variants

of the Illinois general aquatic life use, a modified use, and the secondary contact use based on

alternate RAS lists and two options for ambient temperature regimes in the Lower Des Plaines

River.

Period

RAS 1

Option A8

RAS 1

Option B

9

RAS 1

Option C

w

RAS 1

Option D

1 '

RAS 1

Option E

12

RAS 1

Option F13

January 1-31

38.4/46.6

38.4/46.6

39.5/45.0

39.5/45.0

38.4/46.6

38.4/46.6

February 1-28

41.7/51.7

41.7/51.7

41.0/46.0

41.0/46.0

41.7/51.7

41.7/51.7

March 1-31

47.0/57.3

47.0/57.3

46.0/54.0

46.0/54.0

47.0/57.3

47.0/57.3

April 1-15

54.0/59.9

54.0/59.9

54.0/59.9

54.0/59.9

April 16-30

57.3/67.7

57.3/67.7

56.5/64.0

56.5/64.0

57.3/67.7

57.3/67.7

May 1-15

63.7/71.6

63.7/71.6

63.7/71.6

63.7/71.6

May 16-31

65.1/71.2

65.1/71.2

63.0/68.0

63.0/68.0

65.1/71.2

65.1/71.2

June 1-15

69.8/77.8

69.8/77.8

69.8/77.8

69.8/77.8

June 16-30

85.1/88.7

80.6/84.2

80.6/84.2

85.1/88.7

85.1/88.7

88.3/91.9

July 1-31

85.1/88.7

80.6/84.2

80.6/84.2

85.1/88.7

85.1/88.7

88.3/91.9

August 1-31

85.1/88.7

80.6/84.2

80.6/84.2

85.1/88.7

85.1/88.7

88.3/91.9

September 1-15

85.1/88.7

80.6/84.2

80.6/84.2

85.1/88.7

85.1/88.7

88.3/91.9

September 16-30

69.9/75.7

69.9/75.7

70.5/77.0

77/80.3

69.9/75.7

69.9/75.72

October 1-15

63.7/71.2

63.7/71.2

63.7/71.2

63.7/71.2

October 16-31

59.8/68.0

59.8/68.0

63.0/68.0

63.0/68.0

59.8/68.0

59.8/68.0

November 1-30

53.0/63.6

53.0/63.6

52.5/60.0

52.5/60.0

53.0/63.6

53.0/63.6

December 1-31

43.4/56.9

43.4/56.9

43.0/50.0

43.0/50.0

43.4/56.9

43.4/56.9

General use original RAS (2004 draft report); Cal Sag Rt. 83 site as ambient.

9

General use updated RAS (excludes yellow perch, sauger, walleye); Cal Sag Rt. 83 site as ambient

I°

General use updated RAS (includes yellow perch, sauger, walleye); Holly & Bradley modeling study used as ambient.

n

General use updated RAS (excludes stonecat madtom); Holly & Bradley modeling study used as ambient.

' 2

Modified use RAS (includes silver redhorse); Cal Sag Rt. 83 site as ambient.

13

Secondary Contact/Indigenous Aquatic Life use RAS; Cal Sag Rt. 83 site as ambient.

18

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CABB/MBI

Lower Des Plaines Temperature Criteria Options October 11, 2005

References

Beitinger, T.L., W.A. Bennett, and R.W. McCauley. 2000. Temperature tolerances of

North American freshwater fishes exposed to dynamic changes in temperature.

Env. Biology Fishes 58: 237-275.

Bevelheimer, M. and W. Bennett. 2000. Assessing cumulative stress in fish during chronic

intermittent exposure to high temperatures. Env.

Science & Policy :

S211-S216.

Brown, H.W. 1974. Handbook of the effects of temperature on some North American

fishes. American Electric Power Service Corporation. 431 pp.

Brungs, W.A. and B.R. Jones. 1977. Temperature criteria for freshwater fish: protocol

and procedures. U.S. EPA Ecological Research Series. EPA-600/3-77-061. 136 pp.

Coutant, C.C. 1975. Temperature selection by fish - a factor in power plant impact

assessments, pp. 575-597. in Environmental Effects of Cooling Systems at Nuclear

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Essig, D.A. 1998. The dilemma of applying uniform temperature criteria in a diverse

environment: an issue analysis. Idaho Division of Environmental Quality, Water

Quality Assessment and Standards Bureau, Boise, ID. 29 pp.

Fry, F.E.J. 1947. The effects of the environment on animal activity. University of

Toronto Studies, Biol. Ser.

44: 91

pp.

Hey and Associates. 2003. Lower Des Plaines river use attainability analysis (draft).

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Hokanson, K.E.F. 1990. A national compendium of freshwater fish and water

temperature data. Vol. II. Temperature requirement data for thirty fishes. U.S.

EPA, Office of Research and Development, Environmental Research Laboratory,

Duluth, MN. 178 pp.

Hokanson, K.E.F. and W.M. Koenst. 1986. Revised estimates of growth requirements and

lethal temperature limits of juvenile walleyes. Prog. Fish. Cult. 48:90-94.

Holly, F.M., Jr. and A.A. Bradley. 1995. The Upper Illinois Waterway study: summary

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Waterway. Limited Distribution Repoprt No. 327, Iowa Inst. Hydraulic Res.,

Univ. of Iowa, Iowa City, IA. 112 pp.

19

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October 11, 2005

Midwest Biodiversity Institute. 2005. Re-evaluation of the technical justification for

existing Ohio River mainstem temperature criteria. Report to Ohio River Valley

Water Sanitation Commission. Tech. Rept. MBI/05-05-2. Columbus, OH. 56

pp. +

4 appendices.

Ohio Environmental Protection Agency. 1978. Methods and rationale used for

establishing seasonal average and daily maximum temperature limitations as

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Industrial Wastewater, Columbus, OH. 48 pp. + Appendices..

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Science &

Policy 3: S191-S196.

Selong, J. H., T.E. McMahon, A. V. Zale, and F.T. Barrows. 2001. Effect of temperature on

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determining thermal tolerance in fishes.

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American

Fisheries Society

130: 1026-1037.

Smith, M.H. and K.D. Fausch. 1997. Thermal tolerance and vegetation preference of

Arkansas darter and johnny darter for Colorado plains streams. Trans. Am. Fish.

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Wismer, D.A. and A.E. Christie. 1987. Temperature relationships of Great Lakes fishes:

a data compilation. Great Lakes Fishery Commission Special Publication 87-3.

165 pp.

Yoder, C.O. and E.B. Emery. 2004. Updating a temperature criteria methodology for the

Ohio River mainstem, pp. 4-1 to 4-13. in Proceedings from the EPRI Workshop on

316(a) Issues: Technical and Regulatory Considerations: October 16-17, 2003,

EPRI, Palo Alto CA, and American Electric Power Company, Columbus, OH:

2004. 1008476.

20

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CABB/MBI

Lower Des Plaines Temperature Criteria Options

October

11, 2005

Appendix A

Lower Des Plaines River

Optimum, Growth, Upper Avoidance, and Upper Incipient Lethal Temperatures for Fish

Species Representative of the Illinois General Use, a Modified Use, and the Secondary

Contact/Indigenous Aquatic Life Use (21 tables)

Appendix Tables 1A-G

Appendix Tables 2A-G

Appendix Tables 3A-G

21

---

Appendix Table 1A. Thermal thresholds for original general use RAS list.

Fish Temperature Model -- Selected Species Report

Family

?

Species

Code?

Code

Common Name

Optimum

MWAT

Growth

°C

Upper

Avoidance

°C

UILT

Latin Name

10

004

Longnose Gar

32.5

34.3

34.5

37.8

Lepisosteus osseus

20

001

Skipjack Herring

27.3

29.6

30.7

34.3

Alosa chrysochloris

20

003

Gizzard Shad

30.0

31.9

34.0

35.8

Dorosoma cepedianum

40

002

Bigmouth Buffalo

29.9

32.1

33.3

36.6

Ictiobus cyprinellus

40

004

Smallmouth Buffalo

28.5

31.5

34.1

37.4

Ictiobus bubalus

40

005

Quillback Carpsucker

30.0

31.7

34.2

35.2

Carpiodes cyprinus

40

006

River Carpsucker

29.5

31.4

33.5

35.2

Carpiodes carpio carpio

40

010

Golden Redhorse

25.6

28.2

28.5

33.4

Moxostoma erythrurum

40

011

Smallmouth Redhorse

25.5

28.1

28.5

33.3

Moxostoma macrolepidotum

40

015

Northern Hog Sucker

27.3

29.2

31.6

33.0

Hypentelium nigricans

40

016

White Sucker

26.0

27.8

28.7

31.5

Catostomus commersoni

43

001

Common Carp

31.5

33.4

34.9

37.3

Cyprinus carpio

43

003

Golden Shiner

27.8

29:9

30.7

34.0

Notemigonus crysoleucas

43

020

Emerald Shiner

22.5

25.7

29.8

32.1

Notropis atherinoides

43

028

Spottail Shiner

27.3

30.1

34.5

35.6

Notropis hudsonius

43

032

Spotfin Shiner

29.8

31.9

33.7

36.0

Cyprinella spiloptera

43

043

Bluntnose Minnow

27.5

29.1

31.4

32.4

Pimephales notatus

47

002

Channel Catfish

31.1

33.5

34.8

38.3

Ictalurus punctatus

47

004

Yellow Bullhead

28.3

31.0

31.3

36.4

Ameiurus natalis

77

001

White Crappie

28.6

29.9

30.8

32.5

Pomoxis annularis

77

002

Black Crappie

27.6

30.0

29.7

34.7

Pomoxis nigromaculatus

77

003

Rock Bass

28.1

30.4

33.0

35.0

Ambloplites rupestris

77

004

Smallmouth Bass

30.0

31.6

32.0

34.7

Micropterus dolomieui

77

006

Largemouth Bass

29.1

30.9

31.6

34.5

Micropterus salmoides

77

008

Green Sunfish

27.8

30.3

30.9

35.3

Lepomis cyanellus

77

009

Bluegill Sunfish

30.4

32.4

33.8

36.4

Lepomis macrochirus

77

011

Longear Sunfish

24.1

28.0

31.8

35.9

Lepomis megalotis

77

013

Pumpkinseed Sunfish

28.4

30.5

30.5

34.6

Lepomis gibbosus

80

004

Dusky Darter

22.5

26.0

29.6

32.9

Percina sciera sciera

85

001

Freshwater Drum

29.1

30.5

31.2

33.4

Aplodinotus grunniens

22

---

Appendix Table 2A. Thermal criteria results for orignal general use RAS list.

Fish Temperature Model -- Thermal Thresholds Percentile Report

Category

?

100%?

. 90%

?

75%

?

50%

Optimum?

22.50

?

25.36

?

27.30?

28.35

Growth?

25.70

?

27.98

?

29.30

?

30.45

Avoidance

(UAT)?

28.50?

29.51?

30.70?

31.60

Survival

(LT)?

29.50

?

30.49

?

31.40

?

32.85

Survival (ST)

?

31.50?

32.49?

33.40?

34.85

Species Used

?

N

=?

30

Common Name

Longnose Gar

Skipjack Herring

Gizzard Shad

Bigmouth Buffalo

Smallmouth Buffalo

Quillback Carpsucker

River Carpsucker

Golden Redhorse

Smallmouth Redhorse

Northern Hog Sucker

White Sucker

Common Carp

Golden Shiner

Emerald Shiner

Spottail Shiner

Spotfin Shiner

Bluntnose Minnow

Channel Catfish

Yellow Bullhead

White Crappie

Black Crappie

Rock Bass

Common Name

?

Common Name

Smallmouth Bass

Largemouth Bass

Green Sunfish

Bluegill Sunfish

Longear Sunfish

Pumpkinseed Sunfish

Dusky Darter

Freshwater Drum

23

---

Appendix Table 3A. Thermal tolerance rankings for orignal general use RAS list.

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

Optimum Exceeded

Growth Exceeded

UAT Exceeded

22.5

72.5

Emerald Shiner [1]

22.5

72.5

Dusky Darter [2]

24.1

75.4

Longear Sunfish [3]

25.5

77.9

Smallmouth Redhorse [4]

25.6

78.1

Golden Redhorse [5]

25.7

78.3

Emerald Shiner [1]

26.0

78.8

White Sucker [6]

26.0

78.8

Dusky Darter [2]

27.3

81.1

Skipjack Herring [7]

27.3

81.1

Northern Hog Sucker [8]

27.3

81.1

Spottail Shiner [9]

27.5

81.5

Bluntnose Minnow [10]

27.6

81.7

Black Crappie [11]

27.8

82.0

White Sucker [3]

27.8

82.0

Golden Shiner [12]

27.8

82.0

Green Sunfish [13]

28.0

82.4

Longear Sunfish [4]

28.1

82.6

Smallmouth Redhorse [5]

28.1

82.6

Rock Bass [14]

28.2

82.8

Golden Redhorse [6]

28.3

82.9

Yellow Bullhead [15]

28.4

83.1

Pumpkinseed Sunfish [16]

28.5

83.3

Smallmouth Buffalo [17]

28.5

83.3

Golden Redhorse [1]

28.5

83.3

Smallmouth Redhorse [2]

28.6

83.5

White Crappie [18]

28.7

83.7

White Sucker [3]

29.1

84.4

Bluntnose Minnow [7]

29.1

84.4

Largemouth Bass [19]

29.1

84.4

Freshwater Drum [20]

29.2

84.6

Northern Hog Sucker [8]

29.5

85.1

River Carpsucker [21]

ULIT Exceeded

24

---

Appendix Table 3A. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Tern perature

°C

?

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

29.6

85.3

Skipjack Herring [9]

29.6

85.3

Dusky Darter [4]

29.7

85.5

Black Crappie [5]

29.8

85.6

Emerald Shiner [6]

29.8

85.6

Spotfin Shiner [22]

29.9

85.8

Bigmouth Buffalo [23]

29.9

85.8

Golden Shiner [10]

29.9

85.8

White Crappie [11]

30.0

86.0

Gizzard Shad [24]

30.0

86.0

Quillback Carpsucker [25]

30.0

86.0

Black Crappie [12]

30.0

86.0

Smallmouth Bass [26]

30.1

86.2

Spottail Shiner [13]

30.3

86.5

Green Sunfish [14]

30.4

86.7

Rock Bass [15]

30.4

86.7

Bluegill Sunfish [27]

30.5

86.9

Pumpkinseed Sunfish [16]

30.5

86.9

Pumpkinseed Sunfish [7]

30.5

86.9

Freshwater Drum [17]

30.7

87.3

Skipjack Herring [8]

30.7

87.3

Golden Shiner [9]

30.8

87.4

White Crappie [10]

30.9

87.6

Largemouth Bass [18]

30.9

87.6

Green Sunfish [11]

31.0

87.8

Yellow Bullhead [19]

31.1

88.0

Channel Catfish [28]

31.2

88.2

Freshwater Drum [12]

31.3

88.3

Yellow Bullhead [13]

31.4

88.5

River Carpsucker [20]

31.4

88.5

Bluntnose Minnow [14]

31.5

88.7

Smallmouth Buffalo [21]

31.5

88.7

White Sucker [1]

25

---

Appendix Table 3A. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

31.5

88.7

Common Carp [29]

31.6

88.9

Northern Hog Sucker [15]

31.6

88.9

Smallmouth Bass [22]

31.6

88.9

Largemouth Bass [16]

31.7

89.1

Quillback Carpsucker [23]

31.8

89.2

Longear Sunfish [17]

31.9

89.4

Gizzard Shad [24]

31.9

89.4

Spotfin Shiner [25]

32.0

89.6

Smallmouth Bass [18]

32.1

89.8

Bigmouth Buffalo [26]

32.1

89.8

Emerald Shiner [2]

32.4

90.3

Bluntnose Minnow [3]

32.4

90.3

Bluegill Sunfish [27]

32.5

90.5

Longnose Gar [30]

32.5

90.5

White Crappie [4]

32.9

91.2

Dusky Darter [5]

33.0

91.4

Northern Hog Sucker [6]

33.0

91.4

Rock Bass [19]

33.3

91.9

Bigmouth Buffalo [20]

33.3

91.9

Smallmouth Redhorse [7]

33.4

92.1

Golden Redhorse [8]

33.4

92.1

Common Carp [28]

33.4

92.1

Freshwater Drum [9]

33.5

92.3

River Carpsucker [21]

33.5

92.3

Channel Catfish [29]

33.7

92.7

Spotfin Shiner [22]

33.8

92.8

Bluegill Sunfish [23]

34.0

93.2

Gizzard Shad [24]

34.0

93.2

Golden Shiner [10]

34.1

93.4

Smallmouth Buffalo [25]

34.2

93.6

Quillback Carpsucker [26]

34.3

93.7

Longnose Gar [30]

26

---

Appendix Table 3A. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F

?

Optimum Exceeded

Growth Exceeded? UAT Exceeded

ULIT

Exceeded

34.3

93.7

Skipjack Herring [11]

34.5

94.1

Longnose Gar [27]

34.5

94.1

Spottail Shiner [28]

34.5

94.1

Largemouth Bass [12]

34.6

94.3

Pumpkinseed Sunfish [13]

34.7

94.5

Black Crappie [14]

34.7

94.5

Smallmouth Bass [15]

34.8

94.6

Channel Catfish [29]

34.9

94.8

Common Carp [30]

35.0

95.0

Rock Bass [16]

35.2

95.4

Quillback Carpsucker [17]

35.2

95.4

River Carpsucker [18]

35.3

95.5

Green Sunfish [19]

35.6

96.1

Spottail Shiner [20]

35.8

96.4

Gizzard Shad [21]

35.9

96.6

Longear Sunfish [22]

36.0

96.8

,Spotfin Shiner [23]

36.4

97.5

Yellow Bullhead [24]

36.4

97.5

Bluegill Sunfish [25]

36.6

97.9

Bigmouth Buffalo [26]

37.3

99.1

Common Carp [27]

37.4

99.3

Smallmouth Buffalo [28]

37.8

100.0

Longnose Gar [29]

38.3

100.9

Channel Catfish [30]

27

---

Appendix Table 1 B. Thermal thresholds for general use RAS alternate list 1.

Fish Temperature Model -- Selected Species Report

Family

?

Species

Code

?

Code

Common Name

Optimum

°C

MWAT

Growth

°C

Upper

Avoidance

°C

UILT

°C

Latin Name

10

004

Longnose Gar

32.5

34.3

34.5

37.8

Lepisosteus osseus

20

001

Skipjack Herring

27.3

29.6

30.7

34.3

Alosa chrysochloris

20

003

Gizzard Shad

30.0

31.9

34.0

35.8

Dorosoma cepedianum

37

003

Northern Pike

21.8

25.3

28.9

32.2

Esox lucius

40

002

Bigmouth Buffalo

29.9

32.1

33.3

36.6

Ictiobus cyprinellus

40

004

Smallmouth Buffalo

28.5

31.5

34.1

37.4

Ictiobus bubalus

40

005

Quillback Carpsucker

30.0

31.7

34.2

35.2

Carpiodes cyprinus

40

006

River Carpsucker

29.5

31.4

33.5

35.2

Carpiodes carpio carpio

40

010

Golden Redhorse

25.6

28.2

28.5

33.4

Moxostoma erythrurum

40

011

Smallmouth Redhorse

25.5

28.1

28.5

33.3

Moxostoma macrolepidotum

40

015

Northern Hog Sucker

27.3

29.2

31.6

33.0

Hypentelium nigricans

40

016

White Sucker

26.0

27.8

28.7

31.5

Catostomus commersoni

43

001

Common Carp

31.5

33.4

34.9

37.3

Cyprinus carpio

43

003

Golden Shiner

27.8

29.9

30.7

34.0

Notemigonus crysoleucas

43

013

Creek Chub

28.1

30.0

31.4

33.7

Semotilus atromaculatus

43

020

Emerald Shiner

22.5

25.7

29.8

32.1

Notropis atherinoides

43

023

Redfin Shiner

28.6

30.5

31.9

34.2

Lythrurus umbratilis

43

025

Striped Shiner

28.0

29.9

31.3

33.6

Luxilus chrysocephalus

43

028

Spottail Shiner

27.3

30.1

34.5

35.6

Notropis hudsonius

43

032

Spotfin Shiner

29.8

31_.9

.

33.7

36.0

Cyprinella spiloptera

43

033

Bigmouth Shiner

29.0

30.9

32.3

34.6

Notropis dorsalis

43

034

Sand Shiner

29.4

31.3

32.7

35.0

Notropis stramineus

43

042

Fathead Minnow

27.7

30.0

31.5

34.5

Pimephales promelas

43

043

Bluntnose Minnow

27.5

29.1

31.4

32.4

Pimephales notatus

43

044

Stoneroller

28.2

30.6

33.0

35.5

Campostoma anomalum

47

002

Channel Catfish

31.1

33.5

34.8

38.3

Ictalurus punctatus

47

004

Yellow Bullhead

28.3

31.0

31.3

36.4

Ameiurus natalis

47

006

Black Bullhead

27.6

30.2

32.1

35.4

Ameiurus melas

47

007

Flathead Catfish

31.1

33.4

34.7

38.0

Pylodictis olivaris

47

008

Stonecat Madtom

21.2

23.8

25.7

29.0

Noturus flavus

54

002

Blackstripe Topminnow

30.2

32.8

34.7

38.0

Fundulus notatus

70

001

Brook Silversides

25.0

28.3

31.7

35.0

Labidesthes sicculus

28

---

Appendix Table 1B. continued

Fish Temperature Model -- Selected Species Report

Family

?

Species

Optimum

MWAT

Growth

Upper

Avoidance

UILT

Code

?

Code

Common Name

oC

Latin

Name

74

001

White Bass

29.5

31.5

33.3

35.6

Morone chrysops

77

001

White Crappie

28.6

29.9

30.8

32.5

Pomoxis annularis

77

002

Black Crappie

27.6

30.0

29.7

34.7

Pomoxis nigromaculatus

77

003

Rock Bass

28.1

30.4

33.0

35.0

Ambloplites rupestris

77

004

Smallmouth Bass

30.0

31.6

32.0

34.7

Micropterus dolomieui

77

006

Largemouth Bass

29.1

30.9

31.6

34.5

Micropterus salmoides

77

008

Green Sunfish

27.8

30.3

30.9

35.3

Lepomis cyanellus

77

009

Bluegill Sunfish

30.4

32.4

33.8

36.4

Lepomis macrochirus

77

010

Orangespotted Sunfish

28.7

30.9

31.3

35.4

Lepomis humilis

77

011

Longear Sunfish

24.1

28.0

31.8

35.9

Lepomis megalotis

77

013

Pumpkinseed Sunfish

28.4

30.5

30.5

34.6

Lepomis gibbosus

80

004

Dusky Darter

22.5

26.0

29.6

32.9

Percina sciera sciera

80

014

Johnny Darter

22.7

26.3

30.3

33.6

Etheostoma nigrum

80

024

Fantail Darter

19.7

24.1

30.6

32.8

Etheostoma flabellare

85

001

Freshwater Drum

29.1

30.5

31.2

33.4

Aplodinotus grunniens

---

Appendix Table 2B. Thermal criteria results for general use RAS alternate list 1.

Fish Temperature Model -- Thermal Thresholds Percentile Report

Category

100%?

90%?

75%

50%

Optimum

19.70

?

22.62

?

27.30

28.20

Growth

23.80

?

26.18

?

29.15

30.40

Avoidance (UAT)

25.70

?

29.32

?

30.70

31.60

Survival (LT)

27.00?

30.46

?

31.50

32.70

Survival

(ST)

29.00?

32.46

?

33.50

34.70

Species Used

N =?

47

Common Name

Common Name

Common Name

Longnose Gar

Fathead Minnow

Johnny Darter

Skipjack Herring

Bluntnose Minnow

Fantail Darter

Gizzard Shad

Stoneroller

Freshwater Drum

Northern Pike

Channel Catfish

Bigmouth Buffalo

Yellow Bullhead

Smallmouth Buffalo

Black Bullhead

Quillback Carpsucker .

Flathead Catfish

River Carpsucker

Stonecat Madtom

Golden Redhorse

Blackstripe Topminnow

Smallmouth Redhorse

Brook Silversides

Northern Hog Sucker

White Bass

White Sucker

White Crappie

Common Carp

Black Crappie

Golden Shiner

Rock Bass

Creek Chub

Smallmouth Bass

Emerald Shiner

Largemouth Bass

Redfin Shiner

Green Sunfish

Striped Shiner

Bluegill Sunfish

Spottail Shiner

Orangespotted Sunfish

Spotfin Shiner

Longear Sunfish

Bigmouth Shiner

Pumpkinseed Sunfish

Sand Shiner

Dusky Darter

30

---

Appendix Table 3B. Thermal tolerance rankings for general use RAS alternate list 1.

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

19.7

67.5

Fantail Darter [1]

21.2

70.2

Stonecat Madtom [2]

21.8

71.2

Northern Pike [3]

22.5

72.5

Emerald Shiner [4]

22.5

72.5

Dusky Darter [5]

22.7

72.9

Johnny Darter [6]

23.8

74.8

Stonecat Madtom [1]

24.1

75.4

Longear Sunfish [7]

24.1

75.4

Fantail Darter [2]

25.0

77.0

Brook Silversides [8]

25.3

77.5

Northern Pike [3]

25.5

77.9

Smallmouth Redhorse [9]

25.6

78.1

Golden Redhorse [10]

25.7

78.3

Emerald Shiner [4]

25.7

78.3

Stonecat Madtom [1]

26.0

78.8

White Sucker [11]

26.0

78.8

Dusky Darter [5]

26.3

79.3

Johnny Darter [6]

27.3

81.1

Skipjack Herring [12]

27.3

81.1

Northern Hog Sucker [13]

27.3

81.1

Spottail Shiner [14]

27.5

81.5

Bluntnose Minnow [15]

27.6

81.7

Black Bullhead [16]

27.6

81.7

Black Crappie [17]

27.7

81.9

Fathead Minnow [.18]

27.8

82.0

White Sucker [7]

27.8

82.0

Golden Shiner [19]

27.8

82.0

Green Sunfish [20]

28.0

82.4

Striped Shiner [21]

28.0

82.4

Longear Sunfish [8]

28.1

82.6

Smallmouth Redhorse [9]

28.1

82.6

Creek Chub [22]

ULIT Exceeded

31

---

Appendix Table 3B. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

28.1

82.6

Rock Bass [23]

28.2

82.8

Golden Redhorse [10]

28.2

82.8

Stoneroller [24]

28.3

82.9

Yellow Bullhead [25]

28.3

82.9

Brook Silversides [11]

28.4

83.1

Pumpkinseed Sunfish [26]

28.5

83.3

Smallmouth Buffalo [27]

28.5

83.3

Golden Redhorse [2]

28.5

83.3

Smallmouth Redhorse [3]

28.6

83.5

Redfin Shiner [28]

28.6

83.5

White Crappie [29]

28.7

83.7

White Sucker [4]

28.7

83.7

Orangespotted Sunfish [30]

28.9

84.0

Northern Pike [5]

29.0

84.2

Bigmouth Shiner [31]

29.0

84.2

Stonecat'Madtom [1]

29.1

84.4

Bluntnose Minnow [12]

29.1

84.4

Largemouth Bass [32]

29.1

84.4

Freshwater Drum [33]

29.2

84.6

Northern Hog Sucker [13]

29.4

84.9

Sand Shiner [34]

29.5

85.1

River Carpsucker [35]

29.5

85.1

White Bass [36]

29.6

85.3

Skipjack Herring [14]

29.6

85.3

Dusky Darter [6]

29.7

85.5

Black Crappie [7]

29.8

85.6

Emerald Shiner [8]

29.8

85.6

Spotfin Shiner [37]

29.9

85.8

Bigmouth Buffalo [38]

29.9

85.8

Golden Shiner [15]

29.9

85.8

Striped Shiner [16]

29.9

85.8

White Crappie [17]

32

---

Appendix Table 3B. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

30.0

86.0

Gizzard Shad [39]

30.0

86.0

Quillback Carpsucker [40]

30.0

86.0

Creek Chub [18]

30.0

86.0

Fathead Minnow [19]

30.0

86.0

Black Crappie [20]

30.0

86.0

Smallmouth Bass [41]

30.1

86.2

Spottail Shiner [21]

30.2

86.4

Black Bullhead [22]

30.2

86.4

Blackstripe Topminnow [42]

30.3

86.5

Green Sunfish [23]

30.3

86.5

Johnny Darter [9]

30.4

86.7

Rock Bass [24]

30.4

86.7

Bluegill Sunfish [43]

30.5

86.9

Redfin Shiner [25]

30.5

86.9

Pumpkinseed Sunfish [26]

30.5

86.9

Pumpkinseed Sunfish [10]

30.5

86.9

Freshwater Drum [27]

30.6

87.1

Stoneroller [28]

30.6

87.1

Fantail Darter [11]

30.7

87.3

Skipjack Herring [12]

30.7

87.3

Golden Shiner [13]

30.8

87.4

White Crappie [14]

30.9

87.6

Bigmouth Shiner [29]

30.9

87.6

Largemouth Bass [30]

30.9

87.6

Green Sunfish [15]

30.9

87.6

Orangespotted Sunfish [31]

31.0

87.8

Yellow Bullhead [32]

31.1

88.0

Channel Catfish [44]

31.1

88.0

Flathead Catfish [45]

31.2

88.2

Freshwater Drum [16]

31.3

88.3

Striped Shiner [17]

31.3

88.3

Sand Shiner [33]

ULIT Exceeded

33

---

Appendix Table 3B. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

31.3

88.3

Yellow Bullhead [18]

31.3

88.3

Orangespotted Sunfish [19]

31.4

88.5

River Carpsucker [34]

31.4

88.5

Creek Chub [20]

31.4

88.5

Bluntnose Minnow [21]

31.5

88.7

Smallmouth Buffalo [35]

31.5

88.7

White Sucker [2]

31.5

88.7

Common Carp [46]

31.5

88.7

Fathead Minnow [22]

31.5

88.7

White Bass [36]

31.6

88.9

Northern Hog Sucker [23]

31.6

88.9

Smallmouth Bass [37]

31.6

88.9

Largemouth Bass [24]

31.7

89.1

Quillback Carpsucker [38]

31.7

89.1

Brook Silversides [25]

31.8

89.2

Longear Sunfish [26]

31.9

89.4

Gizzard Shad [39]

31.9

89.4

Redfin Shiner [27]

31.9

89.4

Spotfin Shiner [40]

32.0

89.6

Smallmouth Bass [28]

32.1

89.8

Bigmouth Buffalo [41]

32.1

89.8

Emerald Shiner [3]

32.1

89.8

Black Bullhead [29]

32.2

90.0

Northern Pike [4]

32.3

90.1

Bigmouth Shiner [30]

32.4

90.3

Bluntnose Minnow [5]

32.4

90.3

Bluegill Sunfish [42]

32.5

90.5

Longnose Gar [47]

32.5

90.5

White Crappie [6]

32.7

90.9

Sand Shiner [31]

32.8

91.0

Blackstripe Topminnow [43]

32.8

91.0

Fantail Darter [7]

34

---

Appendix Table 3B. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

32.9

91.2

Dusky Darter [8]

33.0

91.4

Northern Hog Sucker [9]

33.0

91.4

Stoneroller [32]

33.0

91.4

Rock Bass [33]

33.3

91.9

Bigmouth Buffalo [34]

33.3

91.9

Smallmouth Redhorse [10]

33.3

91.9

White Bass [35]

33.4

92.1

Golden Redhorse [11]

33.4

92.1

Common Carp [44]

33.4

92.1

Flathead Catfish [45]

33.4

92.1

Freshwater Drum [12]

33.5

92.3

River Carpsucker [36]

33.5

92.3

Channel Catfish [46]

33.6

92.5

Striped Shiner [13]

33.6

92.5

Johnny Darter [14]

33.7

92.7

Creek Chub [15]

33.7

92.7

Spotfin Shiner [37]

33.8

92.8

Bluegill Sunfish [38]

34.0

93.2

Gizzard Shad [39]

34.0

93.2

Golden Shiner [16]

34.1

93.4

Smallmouth Buffalo [40]

34.2

93.6

Quillback Carpsucker [41]

34.2

93.6

Redfin Shiner [17]

34.3

93.7

Longnose Gar [47]

34.3

93.7

Skipjack Herring [18]

34.5

94.1

Longnose Gar [42]

34.5

94.1

Spottail Shiner [43]

34.5

94.1

Fathead Minnow [19]

34.5

94.1

Largemouth Bass [20]

34.6

94.3

Bigmouth Shiner [21]

34.6

94.3

Pumpkinseed Sunfish [22]

34.7

94.5

Flathead Catfish [44]

35

---

Appendix Table 3B. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F?

Optimum Exceeded

? Growth Exceeded

UAT Exceeded

ULIT Exceeded

34.7

94.5

Blackstripe Topminnow [45]

34.7

94.5

Black Crappie [23]

34.7

94.5

Smallmouth Bass [24]

34.8

94.6

Channel Catfish [46]

34.9

94.8

Common Carp [47]

35.0

95.0

Sand Shiner [25]

35.0

95.0

Brook Silversides [26]

35.0

95.0

Rock Bass [27]

35.2

95.4

Quillback Carpsucker [28]

35.2

95.4

River Carpsucker [29]

35.3

95.5

Green Sunfish [30]

35.4

95.7

Black Bullhead [31]

35.4

95.7

Orangespotted Sunfish [32]

35.5

95.9

Stoneroller [33]

35.6

96.1

Spottail Shiner [34]

35.6

96.1

White Bass [35]

35.8

96.4

Gizzard Shad [36]

35.9

96.6

Longear Sunfish [37]

36.0

96.8

Spotfin Shiner [38]

36.4

97.5

Yellow Bullhead [39]

36.4

97.5

Bluegill Sunfish [40]

36.6

97.9

Bigmouth Buffalo [41]

37.3

99.1

Common Carp [42]

37.4

99.3

Smallmouth Buffalo [43]

37.8

100.0

Longnose Gar [44]

38.0

100.4

Flathead Catfish [45]

38.0

100.4

Blackstripe Topminnow [46]

38.3

100.9

Channel Catfish [47]

36

---

Appendix Table 1C. Thermal thresholds for general use RAS alternate list 2.

Fish Temperature Model -- Selected Species Report

Family?

Species

Code

?

Code

Common Name

Optimum

°C

MWAT

Growth

°C

Upper

Avoidance

°C

UILT

°C

Latin Name

10

004

Longnose Gar

32.5

34.3

34.5

37.8

Lepisosteus osseus

20

001

Skipjack Herring

27.3

29.6

30.7

34.3

Alosa chrysochloris

20

003

Gizzard Shad

30.0

31.9

34.0

35.8

Dorosoma cepedianum

37

003

Northern Pike

21.8

25.3

28.9

32.2

Esox lucius

40

002

Bigmouth Buffalo

29.9

32.1

33.3

36.6

Ictiobus cyprinellus

40

004

Smallmouth Buffalo

28.5

31.5

34.1

37.4

Ictiobus bubalus

40

005

Quillback Carpsucker

30.0

31.7

34.2

35.2

Carpiodes cyprinus

40

006

River Carpsucker

29.5

31.4

33.5

35.2

Carpiodes carpio carpio

40

010

Golden Redhorse

25.6

28.2

28.5

33.4

Moxostoma erythrurum

40

011

Smallmouth Redhorse

25.5

28.1

28.5

33.3

Moxostoma macrolepidotum

40

015

Northern Hog Sucker

27.3

29.2

31.6

33.0

Hypentelium nigricans

40

016

White Sucker

26.0

27.8

28.7

31.5

Catostomus commersoni

43

001

Common Carp

31.5

33.4

34.9

37.3

Cyprinus carpio

43

003

Golden Shiner

27.8

29.9

30.7

34.0

Notemigonus crysoleucas

43

013

Creek Chub

28.1

30.0

31.4

33.7

Semotilus atromaculatus

43

020

Emerald Shiner.

22.5

25.7

29.8

32.1

Notropis atherinoides

43

023

Redfin Shiner

28.6

30.5

31.9

34.2

Lythrurus umbratilis

43

025

Striped Shiner

28.0

29.9

31.3

33.6

Luxilus chrysocephalus

43

028

Spottail Shiner

27.3

30.1

34.5

35.6

Notropis hudsonius

43

032

Spotfin Shiner

29.8

31.9

33.7

36.0

Cyprinella spiloptera

43

033

Bigmouth Shiner

29.0

30.9

32.3

34.6

Notropis dorsalis

43

034

Sand Shiner

29.4

31.3

32.7

35.0

Notropis stramineus

43

042

Fathead Minnow

27.7

30.0

31.5

34.5

Pimephales promelas

43

043

Bluntnose Minnow

27.5

29.1

31.4

32.4

Pimephales notatus

43

044

Stoneroller

28.2

30.6

33.0

35.5

Campostoma anomalum

47

002

Channel Catfish

31.1

33.5

34.8

38.3

Ictalurus punctatus

47

004

Yellow Bullhead

28.3

31.0

31.3

36.4

Ameiurus natalis

47

006

Black Bullhead

27.6

30.2

32.1

35.4

Ameiurus melas

47

007

Flathead Catfish

31.1

33.4

34.7

38.0

Pylodictis olivaris

47

008

Stonecat Madtom

21.2

23.8

25.7

29.0

Noturus flavus

54

002

Blackstripe Topminnow

30.2

32.8

34.7

38.0

Fundulus notatus

70

001

Brook Silversides

25.0

28.3

31.7

35.0

Labidesthes sicculus

37

---

Appendix Table 1C. continued

Fish Temperature Model -- Selected Species Report

MWAT

Upper

Family

?

Species

Optimum Growth Avoidance

UILT

Code

?

Code

Common Name

°C

°C

°C

°C

Latin Name

74?

001

White Bass

29.5

31.5

33.3

35.6

Morone chrysops

77

?

001

White Crappie

28.6

29.9

30.8

32.5

Pomoxis annularis

77

?

002

Black Crappie

27.6

30.0

29.7

34.7

Pomoxis nigromaculatus

77?

003

Rock Bass

28.1

30.4

33.0

35.0

Ambloplites rupestris

77

?

004

Smallmouth Bass

30.0

31.6

32.0

34.7

Micropterus dolomieui

77

?

006

Largemouth Bass

29.1

30.9

31.6

34.5

Micropterus salmoides

77?

008

Green Sunfish

27.8

30.3

30.9

35.3

Lepomis cyanellus

77

?

009

Bluegill Sunfish

30.4

32.4

33.8

36.4

Lepomis macrochirus

77?

010

Orangespotted Sunfish

28.7

30.9

31.3

35.4 Lepomis humilis

77

?

011

Longear Sunfish

24.1

28.0

31.8

35.9

Lepomis megalotis

77

?

013

Pumpkinseed Sunfish

28.4

30.5

30.5

34.6

Lepomis gibbosus

80

?

001

Sauger

23.9

26.9

30.3

32.9

Stizostedion canadense

80

?

002

Walleye

22.8

26.2

30.0

32.9 Stizostedion vitreum

80

?

003

Yellow Perch

22.6

26.0

29.8

32.9

Perca flavescens

80?

004

Dusky Darter

22.5

26.0

29.6

32.9

Percina sciera sciera

80

?

014

Johnny Darter

22.7

26.3

30.3

33.6 Etheostoma nigrum

80?

024

Fantail Darter

19.7

24.1

30.6

32.8

Etheostoma flabellare

85?

001

Freshwater Drum

29.1

30.5

31.2

33.4 Aplodinotus grunniens

---

Appendix Table 2C. Thermal criteria results for general use RAS alternate list 2.

Fish Temperature Model -- Thermal Thresholds Percentile Report

Category

100%

?

90%

?

75%

50%

Optimum

19.70

?

22.59

?

25.70

28.10

Growth

23.80

?

26.00

?

28.23

30.25

Avoidance

(UAT)

25.70?

29.53

?

30.53

31.55

Survival

(LT)

27.00

?

.30.49?

31.33

32.65

Survival

(ST)

29.00?

32.49

?

33.33

34.65

Species Used

N =

?

50

Common Name

Common Name

Common Name

Longnose Gar

Fathead Minnow

Walleye

Skipjack Herring

Bluntnose Minnow

Yellow Perch

Gizzard Shad

Stoneroller

Dusky Darter

Northern Pike

Channel Catfish

Johnny Darter

Bigmouth Buffalo

Yellow Bullhead

Fantail Darter

Smallmouth Buffalo

Black Bullhead

Freshwater Drum

Quillback Carpsucker

Flathead Catfish

River Carpsucker

Stonecat Madtom

Golden Redhorse

Blackstripe Topminnow

Smallmouth Redhorse

Brook Silversides

Northern Hog Sucker

White Bass

White Sucker

White Crappie

Common Carp

Black Crappie

Golden Shiner

Rock Bass

Creek Chub

Smallmouth Bass

Emerald Shiner

Largemouth Bass

Redfin Shiner

Green Sunfish

Striped Shiner

Bluegill Sunfish

Spottail Shiner

Orangespotted Sunfish

Spotfin Shiner

Longear Sunfish

Bigmouth Shiner

Pumpkinseed Sunfish

Sand Shiner

Sauger

39

---

Appendix Table 3C. Thermal tolerance rankings for general use RAS alternate list 2.

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

19.7

67.5

Fantail Darter [1]

21.2

70.2

Stonecat Madtom [2]

21.8

71.2

Northern Pike [3]

22.5

72.5

Emerald Shiner [4]

22.5

72.5

Dusky Darter [5]

22.6

72.7

Yellow Perch [6]

22.7

72.9

Johnny Darter [7]

22.8

73.0

Walleye [8]

23.8

74.8

Stonecat Madtom [1]

23.9

75.0

Sauger [9]

24.1

75.4

Longear Sunfish [10]

24.1

75.4

Fantail Darter [2]

25.0

77.0

Brook Silversides [11]

25.3

77.5

Northern Pike [3]

25.5

77.9

Smallmouth Redhorse [12]

25.6

78.1

Golden Redhorse [13]

25.7

78.3

Emerald Shiner [4]

25.7

78.3

Stonecat Madtom [1]

26.0

78.8

White Sucker [14]

26.0

78.8

Yellow Perch [5]

26.0

78.8

Dusky Darter [6]

26.2

79.2

Walleye [7]

26.3

79.3

Johnny Darter [8]

26.9

80.4

Sauger [9]

27.3

81.1

Skipjack Herring [15]

27.3

81.1

Northern Hog Sucker [16]

27.3

81.1

Spottail Shiner [17]

27.5

81.5

Bluntnose Minnow [18]

27.6

81.7

Black Bullhead [19]

27.6

81.7

Black Crappie [20]

27.7

81.9

Fathead Minnow [21]

27.8

82.0

White Sucker [10]

ULIT Exceeded

40

---

Appendix Table 3C. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

27.8

82.0

Golden Shiner [22]

27.8

82.0

Green Sunfish [23]

28.0

82.4

Striped Shiner [24]

28.0

82.4

Longear Sunfish [11]

28.1

82.6

Smallmouth Redhorse [12]

28.1

82.6

Creek Chub [25]

28.1

82.6

Rock Bass [26]

28.2

82.8

Golden Redhorse [13]

28.2

82.8

Stoneroller [27]

28.3

82.9

Yellow Bullhead [28]

28.3

82.9

Brook Silversides [14]

28.4

83.1

Pumpkinseed Sunfish [29]

28.5

83.3

Smallmouth Buffalo [30]

28.5

83.3

Golden Redhorse [2]

28.5

83.3

Smallmouth Redhorse [3]

28.6

83.5

Redfin Shiner [31]

28.6

83.5

White Crappie [32]

28.7

83.7

White Sucker [4]

28.7

83.7

Orangespotted Sunfish [33]

28.9

84.0

Northern Pike [5]

29.0

84.2

Bigmouth Shiner [34]

29.0

84.2

Stonecat Madtom [1]

29.1

84.4

Bluntnose Minnow [15]

29.1

84.4

Largemouth Bass [35]

29.1

84.4

Freshwater Drum [36]

29.2

84.6

Northern Hog Sucker [16]

29.4

84.9

Sand Shiner [37]

29.5

85.1

River Carpsucker [38]

29.5

85.1

White Bass [39]

29.6

85.3

Skipjack Herring [17]

29.6

85.3

Dusky Darter [6]

29.7

85.5

Black Crappie [7]

41

---

Appendix Table 3C. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

29.8

85.6

Emerald Shiner [8]

29.8

85.6

Spotfin Shiner [40]

29.8

85.6

Yellow Perch [9]

29.9

85.8

Bigmouth Buffalo [41]

29.9

85.8

Golden Shiner [18]

29.9

85.8

Striped Shiner [19]

29.9

85.8

White Crappie [20] .

30.0

86.0

Gizzard Shad [42]

30.0

86.0

Quillback Carpsucker [43]

30.0

86.0

Creek Chub [21]

30.0

86.0

Fathead Minnow [22]

30.0

86.0

Black Crappie [23]

30.0

86.0

Smallmouth Bass [44]

30.0

86.0

Walleye [10]

30.1

86.2

Spottail Shiner [24]

30.2

86.4

Black Bullhead [25]

30.2

86.4

Blackstripe Topminnow [45]

30.3

86.5

Green Sunfish [26]

30.3

86.5

Sauger [11]

30.3

86.5

Johnny Darter [12]

30.4

86.7

Rock Bass [27]

30.4

86.7

Bluegill Sunfish [46]

30.5

86.9

Redfin Shiner [28]

30.5

86.9

Pumpkinseed Sunfish [29]

30.5

86.9

Pumpkinseed Sunfish [13]

30.5

86.9

Freshwater Drum [30]

30.6

87.1

Stoneroller [31]

30.6

87.1

Fantail Darter [14]

30.7

87.3

Skipjack Herring [15]

30.7

87.3

Golden Shiner [16]

30.8

87.4

White Crappie [17]

30.9

87.6

Bigmouth Shiner [32]

ULIT Exceeded

42

---

Appendix Table 3C. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT

Exceeded

30.9

87.6

Largemouth Bass [33]

30.9

87.6

Green Sunfish [18]

30.9

87.6

Orangespotted Sunfish [34]

31.0

87.8

Yellow Bullhead [35]

31.1

88.0

Channel Catfish [47]

31.1

88.0

Flathead Catfish [48]

31.2

88.2

Freshwater Drum [19]

31.3

88.3

Striped Shiner [20]

31.3

88.3

Sand Shiner [36]

31.3

88.3

Yellow Bullhead [21]

31.3

88.3

Orangespotted Sunfish [22]

31.4

88.5

River Carpsucker [37]

31.4

88.5

Creek Chub [23]

31.4

88.5

Bluntnose Minnow [24]

31.5

88.7

Smallmouth Buffalo [38]

31.5

88.7

White Sucker [2]

31.5

88.7

Common Carp [49]

31.5

88.7

Fathead Minnow [25]

31.5

88.7

White Bass [39]

31.6

88.9

Northern Hog Sucker [26]

31.6

88.9

Smallmouth Bass [40]

31.6

88.9

Largemouth Bass [27]

31.7

89.1

Quillback Carpsucker [41]

31.7

89.1

Brook Silversides [28]

31.8

89.2

Longear Sunfish [29]

31.9

89.4

Gizzard Shad [42]

31.9

89.4

Redfin Shiner [30]

31.9

89.4

Spotfin Shiner [43]

32.0

89.6

Smallmouth Bass [31]

32.1

89.8

Bigmouth Buffalo [44]

32.1

89.8

Emerald Shiner [3]

32.1

89.8

Black Bullhead [32]

43

---

Appendix Table 3C. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F

Optimum Exceeded

Growth Exceeded

UAT

Exceeded

ULIT Exceeded

32.2

90.0

Northern Pike [4]

32.3

90.1

Bigmouth Shiner [33]

32.4

90.3

Bluntnose Minnow [5]

32.4

90.3

Bluegill Sunfish [45]

32.5

90.5

Longnose Gar [50]

32.5

90.5

White Crappie [6]

32.7

90.9

Sand Shiner [34]

32.8

91.0

Blackstripe Topminnow [46]

32.8

91.0

Fantail Darter [7]

32.9

91.2

Sauger [8]

32.9

91.2

Walleye [9]

32.9

91.2

Yellow Perch [10]

32.9

91.2

Dusky Darter [11]

33.0

91.4

Northern Hog Sucker [12]

33.0

91.4

Stoneroller [35]

33.0

91.4

Rock Bass [36]

33.3

91.9

Bigmouth Buffalo [37]

33.3

91.9

Smallmouth Redhorse [13]

33.3

91.9

White Bass [38]

33.4

92.1

Golden Redhorse [14]

33.4

92.1

Common Carp [47]

33.4

92.1

Flathead Catfish [48]

33.4

92.1

Freshwater Drum [15]

33.5

92.3

River Carpsucker [39]

33.5

92.3

Channel Catfish [49]

33.6

92.5

Striped Shiner [16]

33.6

92.5

Johnny Darter [17]

33.7

92.7

Creek Chub [18]

33.7

92.7

Spotfin Shiner [40]

33.8

92.8

Bluegill Sunfish [41]

34.0

93.2

Gizzard Shad [42]

34.0

93.2

Golden Shiner [19]

44

---

Appendix Table 3C. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F?

Optimum Exceeded

Growth Exceeded

.UAT Exceeded

ULIT Exceeded

34.1

93.4

Smallmouth Buffalo [43]

34.2

93.6

Quillback Carpsucker [44]

34.2

93.6

Redfin Shiner [20]

34.3

93.7

Longnose Gar [50]

34.3

93.7

Skipjack Herring [21]

34.5

94.1

Longnose Gar [45]

34.5

94.1

Spottail Shiner [46]

34.5

94.1

Fathead Minnow [22]

34.5

94.1

Largemouth Bass [23]

34.6

94.3

Bigmouth Shiner [24]

34.6

94.3

Pumpkinseed Sunfish [25]

34.7

94.5

Flathead Catfish [47]

34.7

94.5

Blackstripe Topminnow [48]

34.7

94.5

Black Crappie [26]

34.7

94.5

Smallmouth Bass [27]

34.8

94.6

Channel Catfish [49]

34.9

94.8

Common Carp [50]

35.0

95.0

Sand Shiner [28]

35.0

95.0

Brook Silversides [29]

35.0

95.0

Rock Bass [30]

35.2

95.4

Quillback Carpsucker [31]

35.2

95.4

River Carpsucker [32]

35.3

95.5

Green Sunfish [33]

35.4

95.7

Black Bullhead [34]

35.4

95.7

Orangespotted Sunfish [35]

35.5

95.9

Stoneroller [36]

35.6

96.1

Spottail Shiner [37]

35.6

96.1

White Bass [38]

35.8

96.4

Gizzard Shad [39]

35.9

96.6

Longear Sunfish [40]

36.0

96.8

Spotfin Shiner [41]

36.4

97.5

Yellow Bullhead [42]

45

---

Appendix Table 3C. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded? UAT Exceeded

ULIT Exceeded

36.4

97.5

Bluegill Sunfish [43]

36.6

97.9

Bigmouth Buffalo [44]

37.3

99.1

Common Carp [45]

37.4

99.3

Smallmouth Buffalo [46]

37.8

100.0

Longnose Gar [47]

38.0

100.4

Flathead Catfish [48]

38.0

100.4

Blackstripe Topminnow [49]

38.3

100.9

Channel Catfish [50]

46

---

Appendix Table 1D Thermal thresholds for general use RAS alternate list 3.

Fish Temperature Model -- Selected Species Report

Family?

Species

Code?

Code

Common Name

Optimum

°C

MWAT

Growth

°C

Upper

Avoidance

°C

UILT

°C

Latin Name

10

004

Longnose Gar

32.5

34.3

34.5

37.8

Lepisosteus osseus

20

001

Skipjack Herring

27.3

29.6

30.7

34.3

Alosa chrysochloris

20

003

Gizzard Shad

30.0

31.9

34.0

35.8

Dorosoma cepedianum

37

003

Northern Pike

21.8

25.3

28.9

32.2

Esox lucius

40

002

Bigmouth Buffalo

29.9

32.1

33.3

36.6

Ictiobus cyprinellus

40

004

Smallmouth Buffalo

28.5

31.5

34.1

37.4

Ictiobus bubalus

40

005

Quillback Carpsucker

30.0

31.7

34.2

35.2

Carpiodes cyprinus

40

006

River Carpsucker

29.5

31.4

33.5

35.2

Carpiodes carpio carpio

40

010

Golden Redhorse

25.6

28.2

28.5

33.4

Moxostoma erythrurum

40

011

Smallmouth Redhorse

25.5

28.1

28.5

33.3

Moxostoma macrolepidotum

40

015

Northern Hog Sucker

27.3

29.2

31.6

33.0

Hypentelium nigricans

40

016

White Sucker

26.0

27.8

28.7

31.5

Catostomus commersoni

43

001

Common Carp

31.5

33.4

34.9

37.3

Cyprinus carpio

43

003

Golden Shiner

27.8

29.9

30.7

34.0

Notemigonus crysoleucas

43

013

Creek Chub

28.1

30.0

31.4

33.7

Semotilus atromaculatus

43

020

Emerald Shiner

22.5

25.7

29.8

32.1

Notropis atherinoides

43

023

Redfin Shiner

28.6

30.5

31.9

34.2

Lythrurus umbratilis

43

025

Striped Shiner

28.0

29.9

31.3

33.6

Luxilus chrysocephalus

43

028

Spottail Shiner

27.3

30.1

34.5

35.6

Notropis hudsonius

43

032

Spotfin Shiner

29.8

31.9

33.7

36.0

Cyprinella spiloptera

43

033

Bigmouth Shiner

29.0

30.9

32.3

34.6

Notropis dorsalis

43

034

Sand Shiner

29.4

31.3

32.7

35.0

Notropis stramineus

43

042

Fathead Minnow

27.7

30.0

31.5

34.5

Pimephales promelas

43

043

Bluntnose Minnow

27.5

29.1

31.4

32.4

Pimephales notatus

43

044

Stoneroller

28.2

30.6

33.0

35.5

Campostoma anomalum

47

002

Channel Catfish

31.1

33.5

34.8

38.3

Ictalurus punctatus

47

004

Yellow Bullhead

28.3

31.0

31.3

36.4

Ameiurus natalis

47

006

Black Bullhead

27.6

30.2

32.1

35.4

Ameiurus melas

47

007

Flathead Catfish

31.1

33.4

34.7

38.0

Pylodictis olivaris

54

002

Blackstripe Topminnow

30.2

32.8 .

34.7

38.0

Fundulus notatus

70

001

Brook Silversides

25.0

28.3

31.7

35.0

Labidesthes sicculus

74

001

White Bass

29.5

31.5

33.3

35.6

Morone chrysops

47

---

Appendix Table 1 D. continued

Fish Temperature Model -- Selected Species Report

MWAT

Upper

Family?

Species

Optimum Growth Avoidance

UILT

Code?

Code

Common

Name

°C

°C

°C

°C

Latin Name

77?

001

White Crappie

28.6

29.9

30.8

32.5

Pomoxis annularis

77

?

002

Black Crappie

27.6

30.0

29.7

34.7

Pomoxis nigromaculatus

77

?

003

Rock Bass

28.1

30.4

33.0

35.0

Ambloplites rupestris

77?

004

Smallmouth Bass

30.0

31.6

32.0

34.7

Micropterus dolomieui

77?

006

Largemouth Bass

29.1

30.9

31.6

34.5 Micropterus salmoides

77?

008

Green Sunfish

27.8

30.3

30.9

35.3

Lepomis cyanellus

77

?

009

Bluegill Sunfish

30.4

32.4

33.8

36.4

Lepomis macrochirus

77?

010

Orangespotted Sunfish

28.7

30.9

31.3

35.4

Lepomis humilis

77

?

011

Longear Sunfish

24.1

28.0

31.8

35.9 Lepomis megalotis

77?

013

Pumpkinseed Sunfish

28.4

30.5

30.5

34.6

Lepomis gibbosus

80

?

001

Sauger

23.9

26.9

30.3

32.9

Stizostedion canadense

80

?

002

Walleye

22.8

26.2

30.0

32.9

Stizostedion vitreum

80

?

003

Yellow Perch

22.6

26.0

29.8

32.9

Perca flavescens

80

?

004

Dusky Darter

22.5

26.0

29.6

32.9

Percina sciera sciera

80

?

014

Johnny Darter

22.7

26:3

30.3

33.6

Etheostoma nigrum

80?

024

Fantail Darter

19.7

24.1

30.6

32.8

Etheostoma flabellare

85?

001

Freshwater Drum

29.1

30.5

31.2

33.4

Aplodinotus grunniens

---

Appendix Table 2D. Thermal criteria results for general use RAS alternate list 3.

Fish Temperature Model -- Thermal Thresholds Percentile Report

Category

100%

?

90%

?

75%

50%

Optimum

19.70?

-22.68?

26.00

28.10

Growth

24.10

?

26.16

?

28.30 30.30

Avoidance

(UAT)

28.50?

29.68

?

30.60

31.60

Survival

(LT)

29.50

?

30.74

?

31.40

32.70

Survival

(ST)

31.50?

32.74

?

33.40 34.70

Species Used

N =?

49

Common Name

Common Name

Common Name

Longnose Gar

Fathead Minnow

Yellow Perch

Skipjack Herring

Bluntnose Minnow

Dusky Darter

Gizzard Shad

Stoneroller

Johnny Darter

Northern Pike

Channel Catfish

Fantail Darter

Bigmouth Buffalo

Yellow Bullhead

Freshwater Drum

Smallmouth Buffalo

Black Bullhead

Quillback Carpsucker

Flathead Catfish

River Carpsucker

Blackstripe Topminnow

Golden Redhorse

Brook Silversides

Smallmouth Redhorse

White Bass

Northern Hog Sucker

White Crappie

White Sucker

Black Crappie

Common Carp

Rock Bass

Golden Shiner

Smallmouth Bass

Creek Chub

Largemouth Bass

Emerald Shiner

Green Sunfish

Redfin Shiner

Bluegill Sunfish

Striped Shiner

Orangespotted Sunfish

Spottail Shiner

Longear Sunfish

Spotfin Shiner

Pumpkinseed Sunfish

Bigmouth Shiner

Sauger

Sand Shiner

Walleye

49

---

Appendix Table 3D. Thermal tolerance rankings for general use RAS alternate list 3.

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

19.7

67.5

Fantail Darter [1]

21.8

71.2

Northern Pike [2]

22.5

72.5

Emerald Shiner [3]

22.5

72.5

Dusky Darter [4]

22.6

72.7

Yellow Perch [5]

22.7

72.9

Johnny Darter [6]

22.8

73.0

Walleye [7]

23.9

75.0

Sauger [8]

24.1

75.4

Longear Sunfish [9]

24.1

75.4

Fantail Darter [1]

25.0

77.0

Brook Silversides [10]

25.3

77.5

Northern Pike [2]

25.5

77.9

Smallmouth Redhorse [11]

25.6

78.1

Golden Redhorse [12]

25.7

78.3

Emerald Shiner [3]

26.0

78.8

White Sucker [13]

26.0

78.8

Yellow Perch [4]

26.0

78.8

Dusky Darter [5]

26.2

79.2

Walleye [6]

26.3

79.3

Johnny Darter [7]

26.9

80.4

Sauger [8]

27.3

81.1

Skipjack Herring [14]

27.3

81.1

Northern Hog Sucker [15]

27.3

81.1

Spottail Shiner [16]

27.5

81.5

Bluntnose Minnow [17]

27.6

81.7

Black Bullhead [18]

27.6

81.7

Black Crappie [19]

27.7

81.9

Fathead Minnow [20]

27.8

82.0

White Sucker [9]

27.8

82.0

Golden Shiner [21]

27.8

82.0

Green Sunfish [22]

28.0

82.4

Striped Shiner [23]

ULIT Exceeded

50

---

Appendix Table 3D. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

28.0

82.4

Longear Sunfish [10]

28.1

82.6

Smallmouth Redhorse [11]

28.1

82.6

Creek Chub [24]

28.1

82.6

Rock Bass [25]

28.2

82.8

Golden Redhorse [12]

28.2

82.8

Stoneroller [26]

28.3

82.9

Yellow Bullhead [27]

28.3

82.9

Brook Silversides [13]

28.4

83.1

Pumpkinseed Sunfish [28]

28.5

83.3

Smallmouth Buffalo [29]

28.5

83.3

Golden Redhorse [1]

28.5

83.3

Smallmouth Redhorse [2]

28.6

83.5

Redfin Shiner [30]

28.6

83.5

White Crappie [31]

28.7

83.7

White Sucker [3]

28.7

83.7

Orangespotted Sunfish [32]

28.9

84.0

Northern Pike [4]

29.0

84.2

Bigmouth Shiner [33]

29.1

84.4

Bluntnose Minnow [14]

29.1

84.4

Largemouth Bass [34]

29.1

84.4

Freshwater Drum [35]

29.2

84.6

Northern Hog Sucker [15]

29.4

84.9

Sand Shiner [36]

29.5

85.1

River Carpsucker [37]

29.5

85.1

White Bass [38]

29.6

85.3

Skipjack Herring [16]

29.6

85.3

Dusky Darter [5]

29.7

85.5

Black Crappie [6]

29.8

85.6

Emerald Shiner [7]

29.8

85.6

Spotfin Shiner [39]

29.8

85.6

Yellow Perch [8]

29.9

85.8

Bigmouth Buffalo [40]

ULIT Exceeded

51

---

Appendix Table 3D. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Tern perature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

29.9

85.8

Golden Shiner [17]

29.9

85.8

Striped Shiner [18]

29.9

85.8

White Crappie [19]

30.0

86.0

Gizzard Shad [41]

30.0

86.0

Quillback Carpsucker [42]

30.0

86.0

Creek Chub [20]

30.0

86.0

Fathead Minnow [21]

30.0

86.0

Black Crappie [22]

30.0

86.0

Smallmouth Bass [43]

30.0

86.0

Walleye [9]

30.1

86.2

Spottail Shiner [23]

30.2

86.4

Black Bullhead [24]

30.2

86.4

Blackstripe Topminnow [44]

30.3

86.5

Green Sunfish [25]

30.3

86.5

Sauger [10]

30.3

86.5

Johnny Darter [11]

30.4

86.7

Rock Bass [26]

30.4

86.7

Bluegill Sunfish [45]

30.5

86.9

Redfin Shiner [27]

30.5

86.9

Pumpkinseed Sunfish [28]

30.5

86.9

Pumpkinseed Sunfish [12]

30.5

86.9

Freshwater Drum [29]

30.6

87.1

Stoneroller [30]

30.6

87.1

Fantail Darter [13]

30.7

87.3

Skipjack Herring [14]

30.7

87.3

Golden Shiner [15]

30.8

87.4

White Crappie [16]

30.9

87.6

Bigmouth Shiner [31]

30.9

87.6

Largemouth Bass [32]

30.9

87.6

Green Sunfish [17]

30.9

87.6

Orangespotted Sunfish [33]

31.0

87.8

Yellow Bullhead [34]

U LIT Exceeded

52

---

Appendix Table 3D. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

31.1

88.0

Channel Catfish [46]

31.1

88.0

Flathead Catfish [47]

31.2

88.2

Freshwater Drum [18]

31.3

88.3

Striped Shiner [19]

31.3

88.3

Sand Shiner [35]

31.3

88.3

Yellow Bullhead [20]

31.3

88.3

Orangespotted Sunfish [21]

31.4

88.5

River Carpsucker [36]

31.4

88.5

Creek Chub [22]

31.4

88.5

Bluntnose Minnow [23]

31.5

88.7

Smallmouth Buffalo [37]

31.5

88.7

White Sucker [1]

31.5

88.7

Common Carp [48]

31.5

88.7

Fathead Minnow [24]

31.5

88.7

White Bass [38]

31.6

88.9

Northern Hog Sucker [25]

31.6

88.9

Smallmouth Bass [39]

31.6

88.9

Largemouth Bass [26]

31.7

89.1

Quillback Carpsucker [40]

31.7

89.1

Brook Silversides [27]

31.8

89.2

Longear Sunfish [28]

31.9

89.4

Gizzard Shad [41]

31.9

89.4

Redfin Shiner [29]

31.9

89.4

Spotfin Shiner [42]

32.0

89.6

Smallmouth Bass [30]

32.1

89.8

Bigmouth Buffalo [43]

32.1

89.8

Emerald Shiner [2]

32.1

89.8

Black Bullhead [31]

32.2

90.0

Northern Pike [3]

32.3

90.1

Bigmouth Shiner [32]

32.4

90.3

Bluntnose Minnow [4]

32.4

90.3

Bluegill Sunfish [44]

53

---

Appendix Table 3D. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Tern perature

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

32.5

90.5

Longnose Gar [49]

32.5

90.5

White Crappie [5]

32.7

90.9

Sand Shiner [33]

32.8

91.0

Blackstripe Topminnow [45]

32.8

91.0

Fantail Darter [6]

32.9

91.2

Sauger [7]

32.9

91.2

Walleye [8]

32.9

91.2

Yellow Perch [9]

32.9

91.2

Dusky Darter [10]

33.0

91.4

Northern Hog Sucker [11]

33.0

91.4

Stoneroller [34]

33.0

91.4

Rock Bass [35]

33.3

91.9

Bigmouth Buffalo [36]

33.3

91.9

Smallmouth Redhorse [12]

33.3

91.9

White Bass [37]

33.4

92.1

Golden Redhorse [13]

33.4

92.1

Common Carp [46]

33.4

92.1

Flathead Catfish [47]

33.4

92.1

Freshwater Drum [14]

33.5

92.3

River Carpsucker [38]

33.5

92.3

Channel Catfish [48]

33.6

92.5

Striped Shiner [15]

33.6

92.5

Johnny Darter [16]

33.7

92.7

Creek Chub [17]

33.7

92.7

Spot-fin Shiner [39]

33.8

92.8

Bluegill Sunfish [40]

34.0

93.2

Gizzard Shad [41]

34.0

93.2

Golden Shiner [18]

34.1

93.4

Smallmouth Buffalo [42]

34.2

93.6

Quillback Carpsucker [43]

34.2

93.6

Redfin Shiner [19]

34.3

93.7

Longnose Gar [49]

54

---

Appendix Table 3D. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F

?

Optimum Exceeded

Growth Exceeded?

UAT Exceeded

ULIT Exceeded

34.3

93.7

Skipjack Herring [20]

34.5

94.1

Longnose Gar [44]

34.5

94.1

Spottail Shiner [45]

34.5

94.1

Fathead Minnow [21]

34.5

94.1

Largemouth Bass [22]

34.6

94.3

Bigmouth Shiner [23]

34.6

94.3

Pumpkinseed Sunfish [24]

34.7

94.5

Flathead Catfish [46]

34.7

94.5

Blackstripe Topminnow [47]

34.7

94.5

Black Crappie [25]

34.7

94.5

Smallmouth Bass [26]

34.8

94.6

Channel Catfish [48]

34.9

94.8

Common Carp [49]

35.0

95.0

Sand Shiner [27]

35.0

95.0

Brook Silversides [28]

35.0

95.0

Rock Bass [29]

35.2

95.4

Quillback Carpsucker [30]

35.2

95.4

River Carpsucker [31]

35.3

95.5

Green Sunfish [32]

35.4

95.7

Black Bullhead [33]

35.4

95.7

Orangespotted Sunfish [34]

35.5

95.9

Stoneroller [35]

35.6

96.1

Spottail Shiner [36]

35.6

96.1

White Bass [37]

35.8

96.4

Gizzard Shad [38]

35.9

96.6

Longear Sunfish [39]

36.0

96.8

Spotfin Shiner [40]

36.4

97.5

Yellow Bullhead [41]

36.4

97.5

Bluegill Sunfish [42]

36.6

97.9

Bigmouth Buffalo [43]

37.3

99.1

Common Carp [44]

37.4

99.3

Smallmouth Buffalo [45]

55

---

Appendix Table 3D. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C?

°F?

Optimum Exceeded? Growth Exceeded

?

UAT Exceeded

37.8

?

100.0

38.0?

100.4

38.0?

100.4

38.3

?

100.9

ULIT Exceeded

Longnose Gar [46]

Flathead Catfish [47]

Blackstripe Topminnow [48]

Channel Catfish [49]

56

---

Appendix Table 1 E. Thermal thresholds for modified use RAS 1 list (includes golden redhorse).

Fish Temperature Model -- Selected Species Report

Family

?

Species

Code?

Code

Common Name

Optimum

°C

MWAT

Growth

°C

Upper

Avoidance

°C

UILT

°C

Latin Name

20

003

Gizzard Shad

30.0

31.9

34.0

35.8

Dorosoma cepedianum

37

003

Northern Pike

21.8

25.3

28.9

32.2

Esox lucius

40

002

Bigmouth Buffalo

29.9

32.1

33.3

36.6

Ictiobus cyprinellus

40

010

Golden Redhorse

25.6

28.2

28.5

33.4

Moxostoma erythrurum

40

016

White Sucker

26.0

27.8

28.7

31.5

Catostomus commersoni

43

001

Common Carp

31.5

33.4

34.9

37.3

Cyprinus carpio

43

003

Golden Shiner

27.8

29.9

30.7

34.0

Notemigonus crysoleucas

43

020

Emerald Shiner

22.5

25.7

29.8

32.1

Notropis atherinoides

43

028

Spottail Shiner

27.3

30.1

34.5

35.6

Notropis hudsonius

43

032

Spotfin Shiner

29.8

31.9

33.7

36.0

Cyprinella spiloptera

43

042

Fathead Minnow

27.7

30.0

31.5

34.5

Pimephales promelas

43

043

Bluntnose Minnow

27.5

29.1

31.4

32.4

Pimephales notatus

47

002

Channel Catfish

31.1

33.5

34.8

38.3

Ictalurus punctatus

47

004

Yellow Bullhead

28.3

31.0

31.3

36.4

Ameiurus natalis

47

006

Black Bullhead

27.6

30.2

32.1

35.4

Ameiurus melas

47

007

Flathead Catfish

31.1

33.4

34.7

38.0

Pylodictis olivaris

54

002

Blackstripe Topminnow

30.2

32.8

34.7

38.0

Fundulus notatus

70

001

Brook Silversides

25.0

28.3

31.7

35.0

Labidesthes sicculus

77

002

Black Crappie

27.6

30.0

29.7

34.7

Pomoxis nigromaculatus

77

003

Rock Bass

28.1

30.4

33.0

35.0

Ambloplites rupestris

77

004

Smallmouth Bass

30.0

31.6

32.0

34.7

Micropterus dolomieui

77

006

Largemouth Bass

29.1

30.9

31.6

34.5

Micropterus salmoides

77

008

Green Sunfish

27.8

30.3

30.9

35.3

Lepomis cyanellus

77

009

Bluegill Sunfish

30.4

32.4

33.8

36.4

Lepomis macrochirus

77

013

Pumpkinseed Sunfish

28.4

30.5

30.5

34.6

Lepomis gibbosus

80

002

Walleye

22.8

26.2

30.0

32.9

Stizostedion vitreum

85

001

Freshwater Drum

29.1

30: 5

31.2

33.4

Aplodinotus grunniens

---

Appendix Table 2E. Thermal criteria results for modified use RAS 1 list (includes golden redhorse).

Fish Temperature Model -- Thermal Thresholds Percentile Report

Category

?

.100%

?

90%

?

75%?

50%

Optimum

?

21.80?

24.12

?

27.40

?

28.10

Growth?

25.30

?

27.16?

29.50

?

30.40

Avoidance

(UAT)

?

28.50?

29.38

?

30.60

?

31.60

Survival (LT)

?

29.50

?

30.32

?

31.70?

33.00

Survival (ST)

?

31.50

?

32.32

?

33.70

?

35.00

Species Used

?

N =

?

27

Common Name

?

Common Name

?

Common Name

Gizzard Shad

?

Green Sunfish

Northern Pike

?

Bluegill Sunfish

Bigmouth Buffalo?

Pumpkinseed Sunfish

Golden Redhorse?

Walleye

White Sucker

?

Freshwater Drum

Common Carp

Golden Shiner

Emerald Shiner

Spottail Shiner

Spotfin Shiner

Fathead Minnow

Bluntnose Minnow

Channel Catfish

Yellow Bullhead

Black Bullhead

Flathead Catfish

Blackstripe Topminnow

Brook Silversides

Black Crappie

Rock Bass

Smallmouth Bass

Largemouth Bass

58

---

Appendix Table 3E. Thermal tolerance rankings for modified use RAS 1 list (includes golden redhorse).

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

21.8

71.2

Northern Pike [1]

22.5

72.5

Emerald Shiner [2]

22.8

73.0

Walleye [3]

25.0

77.0

Brook Silversides [4]

25.3

77.5

Northern Pike [1]

25.6

78.1

Golden Redhorse [5]

25.7

78.3

Emerald Shiner [2]

26.0

78.8

White Sucker [6]

26.2

79.2

Walleye [3]

27.3

81.1

Spottail Shiner [7]

27.5

81.5

Bluntnose Minnow [8]

27.6

81.7

Black Bullhead [9]

27.6

81.7

Black Crappie [10]

27.7

81.9

Fathead Minnow [11]

27.8

82.0

White Sucker [4]

27.8

82.0

Golden Shiner [12]

27.8

82.0

Green Sunfish [13]

28.1

82.6

Rock Bass [14]

28.2

82.8

Golden Redhorse [5]

28.3

82.9

Yellow Bullhead [15]

28.3

82.9

Brook Silversides [6]

28.4

83.1

Pumpkinseed Sunfish [16]

28.5

83.3

Golden Redhorse [1]

28.7

83.7

White Sucker [2]

28.9

84.0

Northern Pike [3]

29.1

84.4

Bluntnose Minnow [7]

29.1

84.4

Largemouth Bass [17]

29.1

84.4

Freshwater Drum [18]

29.7

85.5

Black Crappie [4]

29.8

85.6

Emerald Shiner [5]

29.8

85.6

Spotfin Shiner [19]

29.9

85.8

Bigmouth Buffalo [20]

59

---

Appendix Table 3E. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

29.9

85.8

Golden Shiner [8]

30.0

86.0

Gizzard Shad [21]

30.0

86.0

Fathead Minnow [9]

30.0

86.0

Black Crappie [10]

30.0

86.0

Smallmouth Bass [22]

30.0

86.0

Walleye [6]

30.1

86.2

Spottail Shiner [11]

30.2

86.4

Black Bullhead [12]

30.2

86.4

Blackstripe Topminnow[23]

30.3

86.5

Green Sunfish [13]

30.4

86.7

Rock Bass [14]

30.4

86.7

Bluegill Sunfish [24]

30.5

86.9

Pumpkinseed Sunfish [15]

30.5

86.9

Pumpkinseed Sunfish [7]

30.5

86.9

Freshwater Drum [16]

30.7

87.3

Golden Shiner [8]

30.9

87.6

Largemouth Bass [17]

30.9

87.6

Green Sunfish [9]

31.0

87.8

Yellow Bullhead [18]

31.1

88.0

Channel Catfish [25]

31.1

88.0

Flathead Catfish [26]

31.2

88.2

Freshwater Drum [10]

31.3

88.3

Yellow Bullhead [11]

31.4

88.5

Bluntnose Minnow [12]

31.5

88.7

White Sucker [1]

31.5

88.7

Common Carp [27]

31.5

88.7

Fathead Minnow [13]

31.6

88.9

Smallmouth Bass [19]

31.6

88.9

Largemouth Bass [14]

31.7

89.1

Brook Silversides [15]

31.9

89.4

Gizzard Shad [20]

31.9

89.4

Spotfin Shiner [21]

60

---

Appendix Table 3E. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth Exceeded

UAT Exceeded

ULIT Exceeded

32.0

89.6

Smallmouth Bass [16]

32.1

89.8

Bigmouth Buffalo [22]

32.1

89.8

Emerald Shiner [2]

32.1

89.8

Black Bullhead [17]

32.2

90.0

Northern Pike [3]

32.4

90.3

Bluntnose Minnow [4]

32.4

90.3

Bluegill Sunfish [23]

32.8

91.0

Blackstripe Topminnow [24]

32.9

91.2

Walleye [5]

33.0

91.4

Rock Bass [18]

33.3

91.9

Bigmouth Buffalo [19]

33.4

92.1

Golden Redhorse [6]

33.4

92.1

Common Carp [25]

33.4

92.1

Flathead Catfish [26]

33.4

92.1

Freshwater Drum [7]

33.5

92.3

Channel Catfish [27]

33.7

92.7

Spotfin Shiner [20]

33.8

92.8

Bluegill Sunfish [21]

34.0

93.2

Gizzard Shad [22]

34.0

93.2

Golden Shiner [8]

34.5

94.1

Spottail Shiner [23]

34.5

94.1

Fathead Minnow [9]

34.5

94.1

Largemouth Bass [10]

34.6

94.3

Pumpkinseed Sunfish [11]

34.7

94.5

Flathead Catfish [24]

34.7

94.5

Blackstripe Topminnow [25]

34.7

94.5

Black Crappie [12]

34.7

94.5

Smallmouth Bass [13]

34.8

94.6

Channel Catfish [26]

34.9

94.8

Common Carp [27]

35.0

95.0

Brook Silversides [14]

35.0

95.0

Rock Bass [15]

61

---

Appendix Table 3E. continued

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°F?

Optimum Exceeded

?

Growth Exceeded

?

UAT Exceeded

?35.3?

95.5

?

35.4

?

95.7

?

35.6

?

96.1

?

35.8

?

96.4

?

36.0?

96.8

?

36.4

?

97.5

?

36.4

?

97.5

?

36.6?

97.9

?

37.3

?

99.1

?

38.0?

100.4

?

38.0

?

100.4

?

38.3

?

100.9

ULIT Exceeded

Green Sunfish [16]

Black Bullhead [17]

Spottail Shiner [18]

Gizzard Shad [19]

Spotfin Shiner [20]

Yellow Bullhead [21]

Bluegill Sunfish [22]

Bigmouth Buffalo [23]

Common Carp [24]

Flathead Catfish [25]

Blackstripe Topminnow [26]

Channel Catfish [27]

62

---

Appendix Table 1 F. Thermal thresholds for modified use RAS 2 list (excludes golden redhorse).

Fish Temperature Model -- Selected Species Report

Family

?

Species

Code

?

Code

Common Name

Optimum

°C

MWAT

Growth

°C

Upper

Avoidance

°C

UILT

°C

Latin Name

20

003

Gizzard Shad

30.0

31.9

34.0

35.8

Dorosoma cepedianum

37

003

Northern Pike

21.8

25.3

28.9

32.2

Esox lucius

40

002

Bigmouth Buffalo

29.9

32.1

33.3

36.6

Ictiobus cyprinellus

40

016

White Sucker

26.0

27.8

28.7

31.5

Catostomus commersoni

43

001

Common Carp

31.5

33.4

34.9

37.3

Cyprinus carpio

43

003

Golden Shiner

27.8

29.9

30.7

34.0

Notemigonus crysoleucas

43

020

Emerald Shiner

22.5

25.7

29.8

32.1

Notropis atherinoides

43

028

Spottail Shiner

27.3

30.1

34.5

35.6

Notropis hudsonius

43

032

Spotfin Shiner

29.8

31.9

33.7

36.0

Cyprinella spiloptera

43

042

Fathead Minnow

27.7

30.0

31.5

34.5

Pimephales promelas

43

043

Bluntnose Minnow

27.5

29.1

31.4

32.4

Pimephales notatus

47

002

Channel Catfish

31.1

33.5

34.8

38.3

ictalurus punctatus

47

004

Yellow Bullhead

28.3

31.0

31.3

36.4

Ameiurus natalis

47

006

Black Bullhead

27.6

30.2

32.1

35.4

Ameiurus melas

47

007

Flathead Catfish

31.1

33.4

34.7

38.0

Pylodictis olivaris

54

002

Blackstripe Topminnow

30.2

32.8

34.7

38.0

Fundulus notatus

70

001

Brook Silversides

25.0

28.3

31.7

35.0

Labidesthes sicculus

77

002

Black Crappie

27.6

30.0

29.7

34.7

Pomoxis nigromaculatus

77

003

Rock Bass

28.1

30.4

33.0

35.0

Ambloplites rupestris

77

004

Smallmouth Bass

30.0

31.6

32.0

34.7

Micropterus dolomieui

77

006

Largemouth Bass

29.1

30.9

31.6

34.5

Micropterus salmoides

77

008

Green Sunfish

27.8

30.3

30.9

35.3

Lepomis cyanellus

77

009

Bluegill Sunfish

30.4

32.4

33.8

36.4

Lepomis macrochirus

77

013

Pumpkinseed Sunfish

28.4

30.5

30.5

34.6

Lepomis gibbosus

80

002

Walleye

22.8

26.2

30.0

32.9

Stizostedion vitreum

85

001

Freshwater Drum

29.1

30.5

31.2

33.4

Aplodinotus grunniens

---

Appendix Table 2F. Thermal criteria results for modified use RAS 2 list (excludes golden redhorse).

Fish Temperature Model -- Thermal Thresholds Percentile Report

Category

?

100%

?

90%?

75%

?

50%

Optimum?

21.80?

23.90?

27.53

?

28.20

Growth

?

25.30?

27.00

?

29.93?

30.45

Avoidance

(UAT)

?

28.70?

29.75

?

30.75

?

31.65

Survival

(LT)

?

29.50

?

30.30

?

32.13

?

33.00

Survival (ST)

?

31.50

?

32.30

?

34.13?

35.00

Species Used

?

N =?

26

Common Name

?

Common Name

?

Common Name

Gizzard Shad

?

Bluegill Sunfish

Northern Pike

?

Pumpkinseed Sunfish

Bigmouth Buffalo

?

Walleye

White Sucker

?

Freshwater Drum

Common Carp

Golden Shiner

Emerald Shiner

Spottail Shiner

Spotfin Shiner

Fathead Minnow

Bluntnose Minnow

Channel Catfish

Yellow Bullhead

Black Bullhead

Flathead Catfish

Blackstripe Topminnow

Brook Silversides

Black Crappie

Rock Bass

Smallmouth Bass

Largemouth Bass

Green Sunfish

64

---

Appendix Table 3F. Thermal tolerance rankings for modified use RAS 1 list (excludes golden redhorse).

Fish Temperature Model -- Species Thermal Tolerance Rank Report

Temperature

°C

°F

Optimum Exceeded

Growth

Exceeded

UAT

Exceeded

ULIT

Exceeded

21.8

71.2

Northern Pike [1]

22.5

72.5

Emerald Shiner [2]

22.8

73.0 Walleye [3]

25.0

77.0 Brook Silversides [4]

25.3

77.5

Northern Pike [1]

25.7

78.3

Emerald Shiner [2]

26.0

78.8

White Sucker [5]

26.2

79.2

Walleye [3]

27.3

81.1

Spottail Shiner [6]

27.5

81.5

Bluntnose Minnow [7]

27.6

81.7

Black Bullhead [8]

27.6

81.7

Black Crappie [9]

27.7

81.9

Fathead Minnow [10]

27.8

82.0

White Sucker [4]

27.8

82.0

Golden Shiner [11]

27.8

82.0

Green Sunfish [12]

28.1

82.6

Rock Bass [13]

28.3

82.9

Yellow Bullhead [14]

28.3

82.9

Brook Silversides [5]

28.4

83.1

Pumpkinseed Sunfish [15]

28.7