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Carbaryl, Carbofuran, and Methomyl - National Marine Fisheries ...

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type Chinook salmon, it is the 3-month period the sub-yearling smolt spend in the estuary <strong>and</strong><br />

nearshore habitats (i.e., estuary survival). The weight distributions from the organismal model<br />

are converted to length distributions by applying condition factors from data for each modeled<br />

species (cf; 0.0095 for sockeye <strong>and</strong> 0.0115 for all others) as shown in Equation L.<br />

Equation L: length(mm) = ((fish weight(g)/cf)^(1/3))*10<br />

The relationship between length <strong>and</strong> early winter or estuary survival rate was adapted from Zabel<br />

<strong>and</strong> Achord (2004) to match the survival rate for each control model population (Howell et al.<br />

1985, Kostow 1995, Myers et al. 2006). The relationship is based on the length of a sub-yearling<br />

salmon relative to the mean length of other competing sub-yearling salmon of the same species<br />

in the system, Equation D, <strong>and</strong> relates that relative difference to size-dependent survival based<br />

upon Equation S. The values for α <strong>and</strong> resulting size-dependent survival (survival φ) for control<br />

runs for each species are listed in Table 2. The constant α is a species-specific parameter<br />

defined such that it produces the correct control survival φ value when ∆length equals zero.<br />

Equation D: ∆length = fish length(mm) – mean length(mm)<br />

Equation S: Survival φ = (e ( α+(0.0329*∆length)) ) / (1 + e (α+(0.0329*∆length)) )<br />

R<strong>and</strong>omly selecting length values from the normal distribution calculated from the organismal<br />

model output size <strong>and</strong> applying equations 1 <strong>and</strong> 2 generates a size-dependent survival probability<br />

for each fish. This process was replicated 1,000 times for each exposure scenario <strong>and</strong><br />

simultaneously 1,000 times for the paired control scenario <strong>and</strong> results in a mean size-dependent<br />

survival rate for each population. The resulting size-dependent survival rates are inserted in the<br />

calculation of first-year survival in the respective control <strong>and</strong> pesticide-exposed transition<br />

matrices.<br />

The investigation of population-level responses to pesticide exposures uses life history projection<br />

matrix models. Individuals within a population exhibit various growth, reproduction, <strong>and</strong><br />

survivorship rates depending on their developmental or life history stage or age. These age<br />

specific characteristics are depicted in the life history graph (Figure 1A-D) in which transitions<br />

are depicted as arrows. The nonzero matrix elements represent transitions corresponding to<br />

reproductive contribution or survival, located in the top row <strong>and</strong> the subdiagonal of the matrix,<br />

respectively (Figure 1E). The survival transitions in the life history graph are incorporated into<br />

542

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