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Lucy McKergow and Rob Davies-Colley

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1 Lucy McKergow and Rob Davies-Colley
Bugs’n’mud E. coli, turbidity and flow relationships for the Motueka River Lucy McKergow and Rob Davies-Colley

2 Outline background research questions methods results conclusions

3 Background E. coli bacteria MfE & MoH (2003) guidelines
indicator for freshwater recreation source= faecal contamination from warm-blooded animals transport = surface runoff, subsurface flows, direct deposition, re-entrainment of bed sediment MfE & MoH (2003) guidelines <260 cfu/100ml acceptable in small streams turbidity can be used as a surrogate for E. coli

4 Research questions can turbidity be used as a surrogate for E. coli in large rivers? how many E. coli are exported to Tasman Bay?

5 Motueka River At Woodmans Bend 2047 km2 catchment
native + exotic forest 60%, pasture 20% mean flow 82 m3/s median flow 47 m3/s

6 Dataset flood event samples monthly sampling June 03-June 04
sample interval 10 to 30 minutes –auto sampler continuous turbidity - OBS lab turbidity – NTU E. coli – Colilert, most probable number/100 mL monthly sampling May 03 – Dec 05

7 Monitoring period event flow monthly

8 Concentrations Kolmogorov-Smirnov p=0.000 concentrations high during events – particularly on rising limbs of hydrographs

9 E. coli vs flow

10 E. coli vs turbidity

11 18-22 Sep 03 E. coli Flow Turbidity

12 18-21 June 2004 E. coli Flow Turbidity

13 Loads LOADEST USGS model log-linear regression
lnQ, lnQ2, seasonality, decimal time (centred to eliminate collinearity)

14 LOADEST Inst loadobs E = 0.55 r2 = 0.69 mean Ld = 1.4 x 107 #/day
max Ld = 9 x 108 #/day Daily loadpred

15 Conclusions bugs and mud are from different sources
turbidity may not be a consistently useful surrogate for E. coli in large rivers alternative is to use flow


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