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  "name": 
            
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e-aquatic-ecosystem-hevae-instream-value-of-freshwater-rivers-in-nsw",
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e-aquatic-ecosystem-hevae-instream-value-of-freshwater-rivers-in-nsw",
            
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  "notes": "The [NSW riverine High Ecological Value Aquatic Ecosystem 
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  "notes": "The [NSW riverine High Ecological Value Aquatic Ecosystem 
            
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(HEVAE) 
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(HEVAE) 
            
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face-water/monitoring-changes/environmental-value-of-nsw-rivers-hevae) 
30
face-water/monitoring-changes/environmental-value-of-nsw-rivers-hevae) 
            
31
aims to identify and define a range of instream values and levels of 
31
aims to identify and define a range of instream values and levels of 
            
32
importance for freshwater river reaches in NSW. These values will 
32
importance for freshwater river reaches in NSW. These values will 
            
33
assist in the prioritisation of areas for focused water management, to 
33
assist in the prioritisation of areas for focused water management, to 
            
34
assist with water sharing between water users and the environment. The 
34
assist with water sharing between water users and the environment. The 
            
35
water management options include assessment of access and trade rules 
35
water management options include assessment of access and trade rules 
            
36
within Water Sharing Plans (WSPs). The HEVAE product enables NSW 
36
within Water Sharing Plans (WSPs). The HEVAE product enables NSW 
            
37
DCCEEW Water to better meet water management requirements under the 
37
DCCEEW Water to better meet water management requirements under the 
            
38
Water Management Act 2000 and Murray-Darling Basin Plan 
38
Water Management Act 2000 and Murray-Darling Basin Plan 
            
39
2012.\r\n\r\nThe [HEVAE 
39
2012.\r\n\r\nThe [HEVAE 
            
40
toolkit/module-3-guidelines-identifying-high-ecological-value-aquatic) 
40
toolkit/module-3-guidelines-identifying-high-ecological-value-aquatic) 
            
41
was developed by the Commonwealth Government as part of the Australian 
41
was developed by the Commonwealth Government as part of the Australian 
            
42
Aquatic Ecosystem Toolkit and has been adopted by NSW DCCEEW Water as 
42
Aquatic Ecosystem Toolkit and has been adopted by NSW DCCEEW Water as 
            
43
a progressive step to replace other NSW instream value assessments 
43
a progressive step to replace other NSW instream value assessments 
            
44
with a National approach. Although the HEVAE Framework advocates using 
44
with a National approach. Although the HEVAE Framework advocates using 
            
45
five key criteria (Aquatic Ecosystems Task Group 20102a), NSW DCCEEW 
45
five key criteria (Aquatic Ecosystems Task Group 20102a), NSW DCCEEW 
            
46
Water has adopted four criteria, diversity, distinctiveness, 
46
Water has adopted four criteria, diversity, distinctiveness, 
            
47
naturalness and vital habitat. Vital habitat data not able to be 
47
naturalness and vital habitat. Vital habitat data not able to be 
            
48
determined in the coastal HEVAE assessment due to lack of suitable 
48
determined in the coastal HEVAE assessment due to lack of suitable 
            
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data.  Lack of State-wide data prevented inclusion of the fifth 
49
data.  Lack of State-wide data prevented inclusion of the fifth 
            
50
criterion (representativeness). Each of the four criteria relies on 
50
criterion (representativeness). Each of the four criteria relies on 
            
51
state-wide or regional availability of instream value data, to enable 
51
state-wide or regional availability of instream value data, to enable 
            
52
the production of consistent spatial mapping outcomes. Mapping outputs 
52
the production of consistent spatial mapping outcomes. Mapping outputs 
            
53
were derived at the river reach scale and the overall HEVAE scores 
53
were derived at the river reach scale and the overall HEVAE scores 
            
54
identify where the best instream values occur within a catchment. The 
54
identify where the best instream values occur within a catchment. The 
            
55
overall riverine HEVAE outcomes can be examined to determine which 
55
overall riverine HEVAE outcomes can be examined to determine which 
            
56
particular individual values (e.g. a threatened fish species in the 
56
particular individual values (e.g. a threatened fish species in the 
            
57
Distinctiveness criteria) are influencing the final HEVAE 
57
Distinctiveness criteria) are influencing the final HEVAE 
            
58
scores.\r\n\r\nThis [HEVAE 
58
scores.\r\n\r\nThis [HEVAE 
            
59
/0019/207055/applying-the-HEVAE-framework-for-riverine-ecosystems.pdf) 
59
/0019/207055/applying-the-HEVAE-framework-for-riverine-ecosystems.pdf) 
            
60
provides the rationale and describes the methods adapted from the 
60
provides the rationale and describes the methods adapted from the 
            
61
Commonwealth HEVAE Framework for instream value and for each of the 
61
Commonwealth HEVAE Framework for instream value and for each of the 
            
62
four criteria used. Details are provided on the weightings used, and 
62
four criteria used. Details are provided on the weightings used, and 
            
63
scoring approaches, providing the overall HEVAE scores for each river 
63
scoring approaches, providing the overall HEVAE scores for each river 
            
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reach.\r\n\r\nThis dataset contains polyline features defining NSW 
64
reach.\r\n\r\nThis dataset contains polyline features defining NSW 
            
65
freshwater riverine instream value. The dataset enables the inclusion 
65
freshwater riverine instream value. The dataset enables the inclusion 
            
66
of the most up-to-date instream value or asset information to inform 
66
of the most up-to-date instream value or asset information to inform 
            
67
water planning needs in NSW. It also spatially enables the 
67
water planning needs in NSW. It also spatially enables the 
            
68
identification of contemporary instream value data at the river reach 
68
identification of contemporary instream value data at the river reach 
            
69
scale, that can then inform water sharing rules at different scales 
69
scale, that can then inform water sharing rules at different scales 
            
70
required (e.g. management zone or surface water source), The dataset 
70
required (e.g. management zone or surface water source), The dataset 
            
71
facilitates the generation of HEVAE outcomes to inform the risk 
71
facilitates the generation of HEVAE outcomes to inform the risk 
            
72
assessment process and associated strategies in WSPs and WRPs, which 
72
assessment process and associated strategies in WSPs and WRPs, which 
            
73
are requirements under NSW legislation, as well as the Basin 
73
are requirements under NSW legislation, as well as the Basin 
            
74
Plan.\r\n\r\n-----------------------------------\r\n\r\nNote: If you 
74
Plan.\r\n\r\n-----------------------------------\r\n\r\nNote: If you 
            
75
would like to ask a question, make any suggestions, or tell us how you 
75
would like to ask a question, make any suggestions, or tell us how you 
            
76
are using this dataset, please visit the [NSW Water Hub (within SEED) 
76
are using this dataset, please visit the [NSW Water Hub (within SEED) 
            
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which has an online 
77
which has an online 
            
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forum](https://water-hub.seed.nsw.gov.au/thread/search) you can 
78
forum](https://water-hub.seed.nsw.gov.au/thread/search) you can 
            
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join.",
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join.",
            
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