Manning River Estuary Catchment and Management Program 2021-2031

Page 90

6.8 MODIFIED FLOW From an environmental perspective, the full range of flows are necessary to maintain a healthy river system. These include flood flows to scour channels, rework sediments, and inundate floodplains; medium flows to oxygenate water and allow fish passage; and low flows to maintain connectivity and assist the survival of aquatic and riparian flora and fauna.43 Key stressors on flow rates in the Manning include extraction for potable water and irrigation, drought, climate change, sedimentation and infilling of deep pools, and increased peak run-off due to land-clearing and urban development. The total volume of surface water extracted via licenses in the Manning catchment is relatively low, authorised at 78,100 megalitres (ML) from an annual average flow of 2,530,000 ML.44 MidCoast Council’s Water Services team delivers potable water and sewerage services to over 40,000 homes across the LGA. The Manning Water Supply Scheme makes up 90% of water supply in the MidCoast LGA. An entitlement of 17,256 ML/ year is allocated to MidCoast Council for potable town water extracted at Barrington and Bootawa.

43, 44, 45, 47,48: Betterridge & Rabbidge, 2016 46: MidCoast Council, 2020 49: MidCoast Council, 2019

90

The majority of extraction licenses in the catchment are used for irrigation for beef pasture and dairy farms.45 Other irrigators include citrus and vegetable growers, turf farms, equine industries and hobby farms.46 Irrigation in the Manning catchment is below the licensed capacity. Of the 180 irrigation licences only about 20% are active; the balance are ‘sleeper’ licenses.47

Manning River Estuary and Catchment Management Program (ECMP)

Basic landholder rights for stock and domestic use are also allowed. All properties with river/creek frontage are entitled to unregulated access for stock and domestic supplies and can store runoff in surface dams up to a volume of 10% of the rainfall falling on the property. Extraction from the tidal pool has the potential to impact on estuary values and requires further study to ensure adequate protection measures are put in place through the Water Sharing Plan.48 Groundwater extraction via bores can impact on both river base flows and Groundwater Dependent Ecosystems (GDEs). An increase in demand of water from aquifers is likely as a result of increasing insecurity in surface water supply.49 This could be a significant risk during drought when the base flow through much of the system is made up of groundwater. In addition to extraction, drought can be a significant stressor on flow, as was seen in 2017-19 when the Manning experienced the worst drought since instrumental records began in 1880. Manning River flow fell below 50 megalitres per day (ML/d) for 90 days, compared to the previous record of 26 consecutive days. Council received reports of illegal pumping when cease-to-pump rules were in place, which were investigated by the Natural Resources Access Regulator (NRAR).


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Table 9: Contribution of the ECMP to objects of the CM Act

10min
pages 165-168

14 Bibliography

4min
pages 157-158

Appendix 6: MCC land-use strategies aligned to the CM SEPP objectives

9min
pages 178-184

12 Proposed amendments to the CM SEPP

2min
pages 154-155

13 Conclusion

0
page 156

Table 8: Research Program

1min
pages 152-153

11.2 MERI for the ECMP Action Program

1min
page 149

Catchment

4min
pages 142-144

10 Coastal Zone Emergency Sub-Plan

1min
page 140

Actions led by Council

2min
pages 137-138

7.8 Governance Actions

0
page 123

7.5 Aboriginal Custodianship Actions

1min
pages 117-118

7.4 Biodiversity Actions

1min
pages 115-116

Health Actions

5min
pages 109-112

7.1 Stewardship Actions

2min
pages 106-108

Figure 35: The three stages of evaluation

0
pages 104-105

7 Management Actions

4min
pages 102-103

between issues

1min
page 101

6.14 Erosion and Sediment

1min
page 100

6.12 Biodiversity Loss

1min
page 98

6.11 Urban Stormwater and Litter

1min
page 97

20 March 2021

3min
pages 95-96

coastal inundation

1min
page 94

6.9 Entrance Modifications

4min
pages 92-93

Table 4: Key impacts associated with water pollution from diffuse-source runoff

1min
page 88

6.8 Modified Flow

4min
pages 90-91

6.6 Loss and degradation of riparian vegetation

1min
page 85

Acid Sulfate Soil

1min
page 83

6.2 Community Stewardship

1min
page 77

6.4 Loss and degradation of coastal wetlands

1min
page 81

5.2 Manning Threat and Risk Assessment

1min
page 69

Table 1: Gross revenue of major industries in the MidCoast Region

1min
page 64

4.5 Population Projections and land use

0
page 65

Figure 22: Risk ratings for sediment and nutrient loading in drainage units

0
page 68

Figure 17: The sampling location for water quality data

1min
page 58

Figure 20: Manning River chlorophyll-a for the period 2015-2018

1min
pages 61-62

Figure 18: Manning River TN and TP readings from 2015-18

0
page 59

Figure 19: Manning River turbidity for the period 2015-2018

0
page 60

Figure 16: Water quality monitoring sites in the estuary

1min
page 57

4.3 Water Quality

1min
page 56

4.2 Natural assets

5min
pages 52-54

Figure 14: Program Logic Model

1min
page 49

of the Manning catchment

0
page 55

3 Objectives, principles, program logic

1min
page 45

Figure 12: Values our community ascribed to each subcatchment

6min
pages 39-44

Figure 13: Problem tree

0
page 48

3.2 Principles

1min
page 47

2.3 What our community told us

2min
pages 37-38

Coastal Management

2min
pages 20-22

Figure 10: Option for the Manning River ECMP Governance Structure

2min
page 31

1 Introduction Looking after the river we love

1min
page 13

Figure 2: Map of the Planning Areas for the three separate Coastal Management Programs

1min
page 19

2.2 Our stakeholder consultation program

5min
pages 33-35

1.1 About this program

0
page 14

2 Water Quality and Ecosystem

1min
page 7

Characteristics of the estuary and

1min
page 4
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