Abstract:
Sewage sludge is a potentially valuable resource that can enhance both the
structure and fertility of soil. However, it can also harbour enteric pathogens which pose
a significant socio-economic risk to society. Therefore it is important to understand the
factors that govern the persistence of such pathogens in soil, when co-introduced with
sewage sludge, in order to mitigate risk and to further avail of such a valuable resource.
This research aimed to clarify how microbial activity and the presence of sewage sludge
would influence the persistence of co-introduced enteric pathogens in soil. It was
theorised that the addition of sewage sludge to soil would cause the formation of
organic matter (OM) and nutrient-rich niches. Such niches, in turn, would encourage the
enhanced activity of the local soil microbial community, instigating greater competition
for local resources, i.e. a hot spot of microbial activity that would lead to a decline in the
introduced enteric pathogens. It was also hypothesised that the interface between the
soil and sewage sludge may influence such interactions, as the physicochemical
characteristics could affect the extent of exposure and subsequent interactions between
enteric pathogens and the soil microbial community. These theories were investigated
using four different perspectives that linked closely with each other.
In initial studies, two cohorts of microcosms consisting of different proportions
of sewage sludge to soil were inoculated with either E. coli or S. Dublin and
destructively sampled over a 42 day period. E. coli prevailed at greater numbers when
inoculated directly into soil and sewage sludge, whilst it declined to the greatest extent
within mixed microcosms containing 25% sludge. All treatments containing S. Dublin
appeared to decline at a similar rate, which was more linear than the decline observed
within treatments inoculated with E. coli. From these findings, it can be concluded that
there are no direct relationships between the proportion of sludge to soil and its affect
on pathogen survival. A subsequent experiment implemented a similar treatment
strategy, whilst using indigenous sewage sludge E. coli. The use of this microbe
provided data which was more suited to the original premise of this work, as under such
scenarios it would be indigenous sewage sludge E. coli that would be of concern.
Therefore, microcosms consisting of different proportions of sewage sludge, containing
indigenous E. coli, were destructively sampled over a 56 day period. The indigenous
sewage sludge E. coli exhibited a more consistent linear decline after the first week.
However, the indigenous E. coli were again not significantly affected by different
proportions of sewage sludge to soil. It was theorised that this lack of variation in
response to varying proportions of sewage sludge to soil may have been associated with
a lack of available substrate within the system, or some form of partitioning effect
between soil and sewage sludge matrices, which prevented the microbial communities
from interacting.
To further develop these concepts, the effect of two contrasting substrate
amendments and their location (either sewage sludge, soil or within both matrices) was
also investigated in relation to the persistence of sewage sludge-derived E. coli.
Microcosms consisting of both pure samples and mixtures of sewage sludge or soil were
inoculated with sewage sludge-derived E. coli and destructively sampled over a 42 day
period. Respired CO2 and microbial carbon were also quantified. The addition of a
simple substrate, glucose, instigated a peak in microbial respiration and accelerated the
decline of sewage sludge-derived E. coli and also marginally increased the microbial
biomass. This is similar to the original concept proposing that a hot spot of microbial
activity could instigate pathogen die-off. In contrast, amendment with a more complex
substrate, yeast extract, had little effect on the decline of sewage sludge-derived E. coli.
Nor did respiration increase immediately after amendment. There was also no
observable partitioning effects between soil or sewage sludge with either amendment.
This suggests that a lack of available substrate could influence microbial dynamics and
thus the decline of E. coli. To further explore this phenomenon the repeated addition of
glucose and its effect on the survival of sewage sludge-derived E. coli was investigated.
It aimed to highlight the impact of sustained competition for resources on persistence,
whilst mimicking the recurrent input of carbon that occurs in plant/soil systems.
Microcosms consisting of both pure and mixtures of sewage sludge or soil were
inoculated with sewage sludge-derived E. coli and destructively sampled over a period
of 105 days. Respired CO2 and microbial carbon were again analysed. It was found that
the repeated addition of glucose did not cause a significant decline in the survival of
sewage sludge-derived E. coli. Notably, some small increases in E. coli numbers were
observed after the second and third amendments of glucose.
Overall, these findings suggest that hot spots of activity can instigate a decline in
enteric pathogens, though such interactions are dependent upon the availability and
quantity of nutrients and organic carbon within the matrices. These findings could aid in
developing the use of amendments in sewage sludge that would minimise the survival
of enteric pathogens in soil. They also provide a framework which pinpoints the factors
that should be considered when investigating the persistence of enteric pathogens in the
soil environment. Such amendments and knowledge pertaining to the key factors in the
survival of enteric pathogens could further decrease the social and economic risk which
the use of sewage sludge poses when used in agricultural systems.