51813_Sturgeon biodioversity an.PDF

(Martin Jones) #1
and increasingtotalmortality toZ= 0.23willreduce
theEPRvalue lo 20% ofEPRmax(Figure 2). For
paddlefish, increasing the total mortalityratefrom
Z= 0.30(current) toZ= 0.36willreduce theEPR
value to 50% ofEPRmaxand increasing therate toZ
= 0.45willreduce the value to 20% ofEPRmax(Fig-
ure 2).
As a group,chondrosteanpopulations aremore
sensitive to loss inreproductivepotentialcaused by
increases in the mortalityrate of age 7 and older fe-
malesthan arestripedbass,winterflounder, and
bluefishpopulations (Figure 3). The highersensi-
tivity of thechondrosteans tomortality in age 1 and
olderfish is due to acombination of characteristics
that determine their populationdynamics (Table 1).

Figure 3 .Effects ofincreasing the total mortalityrate ( Z ) ofage 1
and olderfemalesabove t h elevelwhenF= 0,on the correspond
The chondrosteans aregenerallylongerlived, are
later maturing and have lower natural mortality

fish. Thechondrosteans do notspawn everyyear
once they reachsexualmaturityand,except for At-
lantic sturgeon and whitesturgeon,havesubstan-
tiallylower fecunditythan theotherthreespecies I
examined. Alifehistorycharacteristicthat inte-
grates individualfecundity,naturalmortality, age at
maturity, and years betweensuccessive spawnings
is the age at which at least 50% of the maximum
lifetime egg production of an age 1 female is

(EPRmax).For white andAtlanticsturgeons, this age
is 3-10 times greater than the equivalent age for
stripedbass,winterflounder, andbluefish(Table 1 ) ;

Table 2.Reduction infishingmortalityrate (F)necessary to

ingpercentage ofthemaximuinlifetime egg production o fa n age
I female for whitesturgeon in theColumbiaRiverbelow the
BonnevilleDam. Atlanticsturgeon in theHudsonRivershort

Lake Ponchartrain, striped bass in the Hudson Rivcr, winter
flounder- in Cape cod Bay, and bluefish along the Atlantic coast.

therefore, theprobability ofsurvivingfrom age 1 to
the age of 50% ofmaximumlifetime egg production
isreduced by a power of3–10for the sturgeons.

rates than striped bass. winter flounder, and blue- nose sturgeon in the lower Connecticut River, paddlefish in

Restricting fishing mortality to offset losses from
achieved when no fishing mortality occurs other sources

For relatively long-lived species such as sturgeons
and paddlefish,a smallreduction infishingmortal-
ity on the age groupsvulnerable to harvest canoff-
set the effects of arelativelylarge reduction in age 0
survival.Thisrelationship ispossiblebecause the
age 0 fish are exposed to the risk of reduced survival
duringonly one year intheirlife;whereas,exposure
to the risk offishingspansmanyyears. As anexam-
ple.suppose the number of age 0 whitesturgeon in
the lowerColumbia River isreduced by 20% due to
contaminanttoxicity. A 20%reduction in age 0 sur-
0 0.370 0 vivalimpliesthat foreveryage 1 femalethat would
5 0.364 2 havesurvived her firstyearoflife, only0.8females

(^1520) 0.3450.352 (^57) value forpotentiallifetime eggproductionfrom 0.8
25 0.339 8 age^1 femaleswith thebaselinefishingmortality
30 0.331 11 rate ofF=0.37is equal tothe lifetime eggproduc-
tionofone age 1 female andafishingmortalityrate
achieveequivalentlifetime eggproduction of an age 1female
whitesturgeon in the ColumbiaRiverbelowBonneyille Dam
when thefraction offemalessurvivingfrom egg to age 1 (S 0 )is
reduced.
Reduction in F needed tomaintain Reduction in F
S 0 ( % ) equivalent lifetime egg (%)
production
10 0.358 (^3) are now survivingunder thealteredconditions.The

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