Case study:Septic Tank Survey in the Clun Forest

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Location: 52° 26' 28.21" N, 3° 9' 36.78" W
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Project overview

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Status Complete
Project web site
Themes Social benefits, Water quality
Country England
Main contact forename Bob
Main contact surname Harris
Main contact user ID User:Dolcoath
Contact organisation Land Life and Livelihoods
Contact organisation web site
Partner organisations
Parent multi-site project
This is a parent project
encompassing the following
projects
No
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Project summary

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The catchment of the Upper Clun and its tributaries is largely unsewered and, although the population density is low, the contribution of septic tanks adding nutrients to the river needs to be better understood. The river is classified to be of high quality but a Special Area of Conservation (SAC) at the lower end is being degraded and there are other signs of freshwater related biodiversity decline. Nutrients play their part, but some of this decline is believed to be due to the deposition of sediment in the riverbed. The river is heavily silt-laden when in spate and this is particularly noticeable in the upper reaches. The steep slopes and high rainfall in the Upper Clun are likely to lead to proportionately high soil erosion and rapid transport with roads acting as conduits and drains as pathways for more rapid transport to the river. This is a community-led and Environment Agency financed review of the state of septic tanks and road drains in the Upper Clun catchment.

Monitoring surveys and results

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A small group of people organised by Land Life and Livelihoods were able to obtain information through questionnaire and interview from 66% of the households with septic tank sewerage systems in the area. In general there was a low degree of awareness of how tanks worked, but people in the locality seem to have readily addressed problems when they have arisen. 52% of tanks are over 30 years old and 37% of soakaway systems being within 25m of a watercourse. The majority of householders (54%) have their tanks desludged frequently (<3 yrs) but a significant proportion (16%) wait 10 yrs or longer. A risk assessment was carried out using the information collected and a ranking list drawn up. Only 3 (2%) systems showed obvious signs of failure and need attention, although the condition of tanks was not physically inspected. Some systems are in high-risk locations but without obvious signs of malfunction and in the absence of supporting water quality data it is difficult to determine whether they are working effectively. Recommendations are made for improvements to the 3 sites and further investigation of the remaining higher-risk sites.

The investigation of the flux of silt and sediment from hillsides and road verges via the road system suggested that roads were major carriers of sediment and that as well as some road drains, overflows from accumulated water and ditches alongside roads also needed to be considered. However, road drains are mostly located in the valley bottoms and so dealing with them is akin to treating the symptom rather than the root causes. The report suggests that a whole catchment analysis of the erosion and sediment transport issues is needed of which managing road drains should play a part.

Lessons learnt

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The overall conclusions are that without water quality data, it is not certain how big an impact on water quality unsewered properties are having. On the face of it, septic tanks do not present as big an issue for river ecology as soil erosion and sediment transport and that a whole catchment approach to understanding the pressures is needed.


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Catchment and subcatchment

Catchment

River basin district Severn
River basin Teme

Subcatchment

River name R Clun - source to conf Folly Bk
Area category 10 - 100 km²
Area (km2)
Maximum altitude category 200 - 500 m
Maximum altitude (m) 496496 m <br />0.496 km <br />49,600 cm <br />
Dominant geology Calcareous
Ecoregion Great Britain
Dominant land cover Improved grassland
Waterbody ID GB109054044000



Site

Name
WFD water body codes GB109054044000
WFD (national) typology
WFD water body name R Clun - source to conf Folly Bk
Pre-project morphology
Reference morphology
Desired post project morphology
Heavily modified water body No
National/international site designation
Local/regional site designations
Protected species present No
Invasive species present No
Species of interest
Dominant hydrology
Dominant substrate
River corridor land use
Average bankfull channel width category
Average bankfull channel width (m)
Average bankfull channel depth category
Average bankfull channel depth (m)
Mean discharge category
Mean annual discharge (m3/s)
Average channel gradient category
Average channel gradient
Average unit stream power (W/m2)


Project background

Reach length directly affected (m)
Project started 2012/01/01
Works started
Works completed
Project completed 2013/05/01
Total cost category
Total cost (k€)
Benefit to cost ratio
Funding sources

Cost for project phases

Phase cost category cost exact (k€) Lead organisation Contact forename Contact surname
Investigation and design
Stakeholder engagement and communication
Works and works supervision
Post-project management and maintenance
Monitoring



Reasons for river restoration

Mitigation of a pressure
Hydromorphology
Biology general protection and improvement of ecosystem health
Physico-chemical water quality, gain evidence about the state of septic tanks, assess the need to consider domestic waste from unsewered properties as a significant source of nutrient to the river, look at the role of discharges from road gullies for sedimentation and turbidity
Other reasons for the project


Measures

Structural measures
Bank/bed modifications
Floodplain / River corridor
Planform / Channel pattern
Other
Non-structural measures
Management interventions
Social measures (incl. engagement) volunteers used to survey householders via face to face interview and questionnaire. Householders with failing septic tank systems were offered expert advice on solutions via consultants. Feedback given to all community through a public meeting.
Other


Monitoring

Hydromorphological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Biological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Physico-chemical quality elements

Element When monitored Type of monitoring Control site used Result
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Any other monitoring, e.g. social, economic

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative


Monitoring documents



Additional documents and videos


Additional links and references

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Supplementary Information

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