Quarry Creek monitoring

Council is monitoring Quarry Creek to check for any potential impacts arising from the construction works at Norman Griffiths Oval.

Council will monitor the site at least weekly. Around specific construction activities or weather events Council may monitor more frequently and will publish the data here.

Week commencing Monday 8 July

Light rainfall recorded early in the week, fining up towards the weekend. 

pH reader reported as not operating properly during the week, only Turbidity recorded until probe can be serviced.

Sediment removal from behind check dams in the creek undertaken with sandbags and coir logs maintained.

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 8/7 10.7 N/A 25.5 N/A Dewatering noted - turbidity level to be observed, NTU of 20.8 recorded at KFAC bridge, max NTU of 26.4 at the Streamwatch site - continue to observe.
Tuesday 9/7 10.3 N/A 23.5 N/A

Good - continue to observe.

Wednesday 10/7 4.9 N/A 31.7* N/A

Downstream sample taken from first pool as contractors working near headwall, dewatering also noted - continue to observe - likely to be local disturbance due to works. NTU of 23.3 recorded at KFAC bridge, 15.2 at the Streamwatch site.

Thursday 11/7 7.4 N/A

11.8

N/A

Good - continue to observe.

Friday 12/7 5.6 N/A 6.2 N/A 

Good - continue to observe.

Traffic lights key

 Turbidity (NTU) 0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6 - 6.4  6.5 - 8.3  8.4 - 9  9.1+

Previous weeks results

Week commencing Monday 1 July

Rainfall recorded at Wahroonga 1-5 July totalled 30.6mm.

Final patching and inspections following the partial pipe collapse during re-lining activities continued throughout the week.

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 1/7 9.7 6.31 16.2 6.25 Continue to monitor.
Tuesday 2/7 10.1 6.16 21.8 6.08

Continue to monitor.

Wednesday 3/7 10 6.3 25 6.22

Continue to monitor.

Turbid water identified escaping through pipe joint. Contractor commissioned to inspect joint and plan emergency repair works.

Thursday 4/7 14.2 6.37

100-500

(morning)

6.5

(morning)

Measurements taken three times during the day - once before and twice after patching works were completed. Water quality showed improvement following patching works.

Mid-morning pH 6.34; Turbidity 27.5 NTU

then

Afternoon pH 6.25; Turbidity 23.2 NTU

Friday 5/7 21.4 5.85 72.7 7.91 

Outlet sample impacted by high turbid flows coming from the side pipe pH7.95; Turbidity 151.6 NTU.

Project team notified and report made to customer service for rangers to inspect high turbidity in the side pipe catchment (Ryde Road Catchment).

Traffic lights key

 Turbidity (NTU) 0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6 - 6.4  6.5 - 8.3  8.4 - 9  9.1+

 

Week commencing Monday 24 June

Rainfall over Saturday 22 – Sunday 23 (18.8 and 17.8mm at Wahroonga).

Partial pipe collapse during re-lining activities resulted in the release of sediment laden water. The incident is still under investigation and response works are ongoing.

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 24/6 12.9 6.53 25* 6.28* *Pipe re-lining working blocking access to outlet sample point. Downstream samples taken from KFAC bridge.
Tuesday 25/6 7.9 6.39 613.6* 6.39*

Section of pipe collapsed during re-lining works, resulting in sediment pollution event that overwhelmed on-site controls. Incident quickly notified to projects team and EPA with actions including establishment of sediment check dams and removal of debris from the pipe implemented asap.

Continue to monitor and clean up following event.

*Pipe re-lining works blocking access to outlet sample point. Downstream samples taken from KFAC bridge.

Wednesday 26/6 17.4 6.7 122.9 6.2*

Turbidity significantly reduced from previous day, however still high following pipe collapse and ongoing clean-up activities.

Turbidity levels quickly improving downstream, Streamwatch site pH 5.87; Turbidity 20.1 NTUs.

Continue to monitor and clean up following event.

*Pipe re-lining works blocking access to outlet sample point. Downstream samples taken from KFAC bridge.

Thursday 27/6 5.5 6.13 51.9* 6.61#

#Sample taken from first pool downstream of headwall.

KFAC Bridge results show good improvement in response to clean up works – pH 6.67; Turbidity 10 NTUs.

Friday 28/6 N/A
N/A

Sample team NA.

Post sediment pollution clean-up works ongoing in first pool downstream from headwall.

Continue to monitor and clean up following event.

Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6 - 6.4  6.5 - 8.3  8.4 - 9  9.1+


Week commencing Monday 17 June

Flows reducing following rainfall over Friday 14 – Saturday 15 (24.8 and 1.4mm at Wahroonga).

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 17/6 9.1 6.75 16.7 6.58 Good - continue to observe.
Tuesday 18/6 7 6.83 14.7 6.37

Site treatment and dewatering during testing, continue to monitor.

Wednesday 19/6 4.7 6.09 4.5 5.93 Turbidity good, pH slightly low with decreased flow, continue to monitor.
Thursday 20/6 4 6.35 106.2 7.42

Downstream sample taken from pool below outlet due to pipe lining works being undertaken at the outlet. Minor activity around the pipe headwall resulted in stirring up sediment in vicinity of the outlet and a high turbidity reading. This high turbidity was localised and reduced quickly downstream to (30.5 at site 3 - KFAC Bridge).

Watch and ensure works do not cause downstream sediment issues.

Friday 21/6 4.6 6.39 3.4 6.09

Turbidity good, pH slightly low with decreased flow, continue to monitor.

Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6  -6.4  6.5 - 8.3  8.4 - 9  9.1+

Week commencing Monday 10 June

Creek flows decreasing following high rainfall during previous week (Thursday 6 June - 51.2mm recorded at Wahroonga) with water treatment and dewatering activities undertaken.

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 10/6 N/A N/A N/A N/A Public holiday
Tuesday 11/6 5.6 7.21 12 6.93

Site treatment and dewatering during sampling.

Wednesday 12/6 4.4 6.56 3.6 6.85 Site treatment and dewatering during sampling.
Thursday 13/6 3.6  6.33 8.5 6.09

Low water levels during testing in morning, dewatering undertaken in afternoon. pH dropping with decreasing flow, continue to monitor.

Friday 14/6 3.3 6.66 3.3 6.15

pH still slightly low with decreased flow, continue to monitor.

Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6  -6.4  6.5 - 8.3  8.4 - 9  9.1+


Week commencing Monday 3 June

High rainfall over the weekend with the site receiving over 100mm of rain (107.2mm recorded at Wahroonga) between Saturday 1 June and Sunday 2 June. This was compounded by further significant rainfall on Thursday 6 June (51.2mm recorded at Wahroonga).

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 3/6 9.2 8.2 15.2 7.94

High flows following heavy rain over the weekend.

Hight turbidity of 51.7 NTU from side pipe near outlet – residential site in catchment lacking sediment control issues reported to rangers.

Tuesday 4/6 4.6 8.02 45.1 8.21

Turbidity of 56.2 NTU from side pipe near outlet – continue to monitor.

Council request contractor to ensure water is removed from site prior to forecast rain.

Wednesday 5/6 N/A N/A  N/A N/A

Sample team not available. 

Contractor removing water from site prior to forecast rain.

Thursday 6/6 5.6  8.41 38.1   7.81

Further rainfall resulting in increasing turbidity – continue to monitor.

Friday 7/6 24.5 8.45 94 7.76

No available flow upstream meant that site could not be sampled.

Dewatering during sampling – low pH reported to project manager and de-watering ceased for investigation and rectification. 

* pH sensor identified for replacement, undertaken 30 May 2024.


Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6  -6.4  6.5 - 8.3  8.4 - 9  9.1+

Week commencing Monday 27 May

Week commencing Monday 27 May

Lack of rainfall and pipe rectification works meant that sampling was restricted this week, as such water quality monitoring results are provided from slightly further downstream.      

It was also identified that the pH sensor would need to be replaced, which was undertaken Thursday 30 May.

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 27/5 N/A – No flow N/A

17.3 (KFAC bridge)
N/A*

pH probe not working.

No available flow upstream and works near the outlet meant that sites could not be sampled.

Ku-ring-gai Fitness and Aquatic Centre (KFAC) Bridge readings provided for downstream.

Tuesday 28/5 N/A – No flow 28.9 (KFAC bridge) N/A*

pH probe not working.

No available flow upstream and works near the outlet meant that sites could not be sampled.

KFAC Bridge readings provided for downstream. Works disturbing sediment, continue to monitor turbidity.

Wednesday 29/5 N/A – No flow 15.2 (pool downstream of outlet) N/A*


pH probe not working.

No available flow upstream meant that site could not be sampled.

Low flows meant site could not be sampled directly at outlet – downstream pool measured as alternative.

Thursday 30/5 N/A - Probe in service

N/A - Probe in service

Friday 31/5 N/A – No flow
13.5 6.01


No available flow upstream meant that site could not be sampled.

Dewatering during sampling – low pH reported to project manager and de-watering ceased for investigation and rectification. 

* pH sensor identified for replacement, undertaken 30 May 2024.


Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6  -6.4  6.5 - 8.3  8.4 - 9  9.1+

Week commencing Monday 20 May

Week commencing Monday 20 May

Lack of rainfall and low flow conditions have resulted in an Iron Bacteria bloom within Quarry Creek.

Iron Bacteria blooms are a natural occurrence in many of Ku-ring-gai’s waterways during low flows and they are not considered to indicate a pollution event. Disturbance of Iron Bacteria whilst undertaking water quality testing can lead to higher turbidity readings, which are not an indication of pollution.

Lower flows also lead to slightly more acidic water, however pH readings above 5.5 will not negatively impact Quarry Creek. pH levels between 5.6 – 6.4 are monitored to ensure levels do not drop too low.

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 20/5 28.2
7.07 44.5 6.03

Water level low, iron bacteria present at downstream sample area, no evidence of sediment laden water.

Turbidity levels decreased downstream and were 22.1 NTU at the Stream Watch monitoring site.  

Continue to monitor.

Tuesday 21/5 24.8 6.87 20.3 6.25

Water level low, iron bacteria present at downstream sample area, no evidence of sediment laden water.

Continue to monitor.

Wednesday 22/5 14.2 6.08 68.2 6.41

Lots of Iron Bacteria in downstream sample area, additional reading done slightly further downstream, returning a result of 12.2 NTU. 

Continue to monitor.

Thursday 23/5 8 5.83 19.6 5.89

Upstream site very low flows, Iron Bacteria remains at downstream site.

Continue to monitor.

Friday 24/5 17.2 6.06 15.5 6.05

Upstream site very low flows, Iron Bacteria remains at downstream site.

Continue to monitor.


Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6  -6.4  6.5 - 8.3  8.4 - 9  9.1+

Week commencing Monday 13 May

Weekend rainfall resulted in moderate turbidity early in the week, that gradually returned to better levels throughout the week.

As high pH detected during site de-watering for a second time the contractor was instructed to stop all de-watering activities immediately and instructed to implement changes to the dewatering procedure.

Council formally reported the contractor’s non-compliance with EMP to the EPA and is working with both the EPA and Contractor to ensure appropriate de-watering procedures are established.

Water monitoring table

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 13/5, 11am 31.4
8.32 20.9 10.48

High pH detected during site de-watering for a second time. Contractor instructed to stop all de-watering activities immediately and to check the system and procedures. Site inspection by Council staff on Monday afternoon result in instructions to change the pump arrangement. 

(Council formally reported incidents on non-compliance with EMP to the EPA on 14/05)

Tuesday 14/5, 10.45am 21.5 7.9 32.4 7.05 Increased Turbidity at outlet, noting similar moderate Turbidity at the side outlet pipe (29.4). Continue monitoring to see if increasing or decreasing flowing light rain on Monday and Tuesday
Wednesday 15/5,12.30pm 14.7 7.45 16.5 7.71 No rain, flows back within healthy range - continue to observe. 
Thursday 16/5, 9am 11.9 7.37 16 8.01 Good – continue to observe.
Friday 17/5, 9am 11.2 7.24 16.4 7.17 Good – continue to observe.


Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6  -6.4  6.5 - 8.3  8.4 - 9  9.1+

Week commencing Monday 6 May

Ongoing repair works and upstream works have contributed to high turbidity levels, however they were quickly addressed. High pH detected during de-watering. Contractor instructed to stop dewatering and review procedures.

  Upstream (Lofberg Rd Channel) Downstream (Norman Griffiths outlet cage)  
   Turbidity (NTU)  pH  NTU  pH  Actions
Monday 6/5, 3pm  29.9
 7.6  78  7.6 Pipe repair works ongoing at time of sample; also noted high NTU from outlet beside the outlet cage (does not pick up NG site drainage) (44)
Tuesday 7/5, 5pm  14.5  7.15  25.2  7.51  Downstream NTU improving following pipe works
Wednesday 8/5, 10am   18 7.73   17.3 7.55   All good – continue to observe
 Thursday 9/5, 3pm  69.7  7.25  40.8  7.58 High turbidity detected coming from upstream parts of the catchment. Investigations into case identify inappropriate controls at a work site on Shaddock Avenue – reported to Council’s Rangers for action.
 Friday 10/5, 9am  10.5  7.37  24.6  10.28 Turbidity good. High pH detected during de-watering. Contractor instructed to stop dewatering and review procedures.

Traffic lights key

 Turbidity (NTU)  0 - 25 25.1 - 40   40.1+    
 pH  <5.5  5.6  -6.4  6.5 - 8.3  8.4 - 9  9.1+

Frequently asked questions

Why are we monitoring the water quality of Quarry Creek? 

Council is monitoring Quarry Creek to check for any potential impacts arising from the construction works at Norman Griffiths Oval. Where potential issues can be identified early, actions can be taken to ensure we avoid irreversible damage to our local environment.

What are the water quality indicators that are being measured? 

The key water quality indicators currently being monitored are Turbidity and pH. 

Turbidity is a measure of how clear or cloudy a liquid is and can be an indicator of sediment being carried by the water. Turbidity is measured in NTUs and turbidity can vary drastically in urban waterways, primarily in response to rainfall, but also in response to soil type and even biological factors.

pH is a measure of how acidic the water is. Our waterways naturally vary in acidity depending on the local geology, soils, amount of urban development and fluctuations in flow and rainfall. Sudden changes in acidity can indicate the potential for a contaminant in the water.

Other indicators being regularly monitored include:

  • Electrical Conductivity – provides an indication on the amount of salts in the water.
  • Dissolved oxygen – whilst dissolved oxygen naturally fluctuates depending on time of day and flow conditions, unusually low levels of dissolved oxygen can be an indicator of a pollution event.

In addition, council has been undertaking additional water sampling that aligns with our Water Quality Monitoring Program. For details on this sampling program please see Water quality monitoring in Ku-ring-gai.

Where are the water samples being taken? 

Water samples are being taken from a number of different locations and catchment areas.

It is noted that it is difficult to sample the direct impacts of the Norman Griffiths Oval construction site on water quality, due to the stormwater connections that occur under the site, providing water contributions for additional catchment areas.

Sampling in the culvert/channel on the upstream side of Lofberg Rd does not include drainage from Lofberg Rd itself or the stormwater line that picks up the catchment around the intersection of Lofberg Rd and Shaddock Ave. It also does not account for the stormwater line that joins the main stormwater line between the existing pit on site and Quarry Creek. This line picks up the catchment around part of Kamilaroy Rd and properties on Andrew Ave.

Water monitoring locations

Norman Griffiths Sportsground_creek monitoring_map1.png
 

Sites

1. Upstream of Norman Griffiths Oval (channel on Lofberg Road).

2. At the Outlet Cage downstream of Norman Griffiths Oval. 

3. Bridge to KFAC, upstream of Prince of Wales Drive

4. Stream Watch Monitoring Site (First Scout Hall bridge)

5. The ‘Lofberg Oval Tributary’ bridge adjacent to the dog-off leash area

6. Pipe beside the outlet cage.

Water catchment areas

Norman Griffiths Sportsground_creek monitoring_map2.png
*Please note catchment areas represented in the map are approximate

What is typical water quality of a creek located in an urban environment?

Urban development exerts significant pressures on local waterways. Due to the location of sewerage infrastructure near watercourses, and an increase in built impervious surfaces, creeks within Ku-ring-gai are increasingly becoming substitute transport pathways for wastes such as stormwater runoff and sewerage effluent. In addition, past land uses such as timber felling, orchards, farming, waste management and mining can have long term impacts. This results in generally poor quality water flowing through our urban creek environments.

Water quality impacts, coupled with the changes in flows that accompany urbanisation result in what is generally known as the ‘urban stream syndrome’ where a reduced level of aquatic biodiversity is able to survive harsh urban environments.  

Pollution in our creeks can generally be categorised as diffuse and point source pollution. Diffuse sources of pollution include factors or activities that may not be significant on an individual scale, but can add up over space or time to be significant, such as litter in our streets. Point-source pollution includes impacts from a specific identifiable source, such as sewer overflows or sediment laden run-off from building sites. 

In response to urban pollution there are ways to help manage stormwater and report possible point source incidents so they can be resolved. Council is currently progressing to become a Water Sensitive City Ku-ring-gai and has been incorporating stormwater harvesting and biofiltration projects to help reduce stormwater impacts in our catchments.

If you notice water pollution such as sediment, paint or chemicals in a local waterway or see someone dumping rubbish or garden waste into or near a waterway call Council 9424 0000.

If you notice sewerage in a waterway or overflowing from any infrastructure, contact Sydney Water on 13 20 90.

What are some factors that can impact water quality readings?

 Factors impacting water quality include (but are not limited to): 

  • Rainfall.
  • Temperature.
  • Groundwater.
  • Sewer overflows.
  • Illegal connection of private sewage to stormwater infrastructure.
  • Stormwater runoff.
  • Industrial discharge.
  • Organic material load.
  • Land contamination.
  • Fuel leaks and spills.
  • Vehicle accidents and material spillage.
  • Fire.
  • Car/boat/house washing.
  • Painting, particularly washing off brushes into a stormwater drain.
  • Pool dewatering.
  • Basement dewatering.
  • Construction sites.
  • Road works.

What measures are Council taking to protect Quarry Creek while work is being carried out at Norman Griffith Oval?

As required for all construction works, the contractors undertaking the work at Norman Griffiths oval are required to do under the provisions contained in an Environmental Management Plan (EMP). The EMP outlines the responsibilities in relation to environmental protection and construction site management, such as the management waste and materials on-site. 

The site is required to detain all site run-off for treatment prior to discharge, however a number of recent breaches have resulted in the loss of sediment laden water from the site.

As such, Council has implemented additional measures to ensure improved protection of Quarry Creek for the remainder of the construction phase of the project. In particular, regular water quality monitoring has commenced and will be continued for the remainder of construction.   

What measures are in place to improve the long term water quality at Quarry Creek?

There are a number of existing and proposed measures to protect and improve the water quality of Quarry Creek.

Bicentennial Park currently contains two Stormwater Quality Improvement Devices (SQUIDs): 

  • The Quarry Creek trash rack is just upstream of Yanko Road and helps to filter coarse sediments, leaf litter and rubbish from the creek.
  • The Lofberg Oval harvesting system and biofilter diverts high (storm) flows from the stormwater system and filters the water to provide irrigation for Lofberg Oval. The vegetated biofilter not only captures sediments and rubbish, it also helps to remove nutrients and heavy metals.  

In addition to the above, the Norman Griffiths Oval upgrade incorporates new measures that will help protect and improve creek water quality including:

  • Filtration of all run-off prior to discharge from the site.
  • New CDS unit, which provides treatment of flows from upstream of Lofberg Road. CDS units capture a wide range of pollutants such as rubbish, leaf litter and sediment.
  • New biofiltration garden that will treat flows passing through the newly installed sub-surface flood detention system. This new biofilter will help to remove nutrients and heavy metals from the stormwater.

In addition, the Kooloona Crescent biofilter garden helps to improve the quality of urban run-off into Quarry Creek, along with all our residents in the catchment who have their own rain gardens and rainwater harvesting tanks.

Contact

Should you require further information please contact sfindlay@krg.nsw.gov.au or 9424 0000.