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. 2019 Oct 2;83(4):e00005-19. doi: 10.1128/MMBR.00005-19

TABLE 4.

Extrinsic biotic factors that influence decay rates in aquatic environments

Extrinsic factor Modifying factor Organism/indicator Notes References
Protozoan predation Temp Culturable E. coli, enterococci, B. fragilis, B. distasonis, and Bacteroides spp. measured by qPCR Higher decay rate at warmer temps coinciding with increased numbers of protozoan grazers. 101, 102, 155, 157
Prey characteristics Culturable E. coli, E. faecalis, Staphylococcus epidermidis, E. coli O157:H7, Klebsiella pneumoniae, S. enterica Higher decay rates for larger allochthonous organisms (e.g., E. coli) than for smaller autochthonous organisms; higher decay rates for Gram-negative bacteria than for Gram-positive bacteria; decay rates also affected by motility and virulence factors. 39, 122, 154, 158, 163, 166
Predator/prey densities Culturable E. coli, E. faecalis Decay rates were positively correlated with bacterial densities. 157, 158
Indigenous microbiota (competition + predation) Location (water/sediment) Culturable E. coli, E. faecalis, E. coli O157:H7, S. enterica Higher decay rate of FIB and pathogens in the water column than in sediment. 45, 122, 156
Water type (fresh/marine) Culturable, E. coli, enterococci Greater decay of FIB in marine water than in freshwater, but the effect of indigenous microbiota was greater in freshwater than in marine water. 27, 28
Nutrients Culturable E. coli Competition and predation increased E. coli decay rates, but higher nutrient levels mitigated these effects. 83, 90
Source E. coli, enterococci (by culture and qPCR), general and human-associated MST markers FIB (from cattle manure and septage) and FIB/MST markers from septage decayed at a lower rate than FIB and MST markers from sewage and human feces. 4, 27