M. Tamayo et al., The relationship between water quality, watermilfoil frequency, and weevildistribution in the state of Washington, J AQUAT PL, 38, 2000, pp. 112-116
During the summer of 1997, we surveyed 50 waterbodies in Washington State t
o determine the distribution of the aquatic weevil Euhrychiopsis lecontei D
ietz. We collected data on water quality and the frequency of occurrence of
water-milfoil species within selected watermilfoil beds to compare the wat
erbodies and determine if they were related to the distribution of E. lecon
tei. We found E. lecontei in 14 waterbodies, most of which were in eastern
Washington. Only one lake with weevils was located in western Washington. W
eevils were associated with both Eurasian (Myriophyllum spicatum L.) and no
rthern watermilfoil (M. sibiricum K). Waterbodies with E. lecontei had sign
ificantly higher (P < 0.05) pH (8.7 +/- 0.2) (mean +/- 2SE), specific condu
ctance (0.3 +/- 0.08 mS cm(-1)) and total alkalinity (132.4 +/- 30.8 mg CaC
O3 L-1). We also found that weevil presence was related to surface water te
mperature and waterbody location (chi (2)(2) = 24.3, P less than or equal t
o 0.001) and of all the models tested, this model provided the best fit (Ho
smer-Lemeshow goodness-of-fit chi (8)(2) = 4.0, P = 0.9). Our results sugge
st that in Washington in waterbodies with pH greater than or equal to8.2 an
d specific conductance greater than or equal to0.2 mS cm(-1). Furthermore,
weevil distribution appears to be correlated with waterbody location (easte
rn versus western Washington) and surface water temperature.