QUININUP HOLDINGS PTY LTD and PROGRAM MANAGER SOUTH WEST REGION AS THE DELEGATE FOR THE MINISTER FOR WATER [2026] WASAT 76
[2026] WASAT 76
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JURISDICTION : STATE ADMINISTRATIVE TRIBUNAL
ACT : RIGHTS IN WATER AND IRRIGATION ACT 1914
(WA)
CITATION : QUININUP HOLDINGS PTY LTD and PROGRAM
MANAGER SOUTH WEST REGION AS THE
DELEGATE FOR THE MINISTER FOR WATER
[2026] WASAT 76
MEMBER : MS C BARTON, MEMBER
MS H BROOKES, SESSIONAL MEMBER
HEARD : 8, 9, 10 AND 11 DECEMBER 2025 AND 19 MARCH
2026
DELIVERED : 2 JULY 2026
FILE NO/S : DR 154 of 2023
BETWEEN : QUININUP HOLDINGS PTY LTD
Applicant
AND
PROGRAM MANAGER SOUTH WEST REGION
AS THE DELEGATE FOR THE MINISTER FOR
WATER
Respondent
Catchwords:
Water licensing - Licence to take water - Licence condition - Farm dam -
Watercourse - Winter take period - Bypass flows - Transitional flows -
Downstream environment - Hydrological features of dam wall - 'Leaky' dam
wall - Whether dam seepage contributes to downstream flow - Ecological water
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requirement - Water-dependent ecosystems - Stream ecology - Aquatic fauna -
Ecological values - Application of water allocation plan - Application of policy -
Consistently applied policy - Whether the take and use of water is ecologically
sustainable - Whether the take and use of water is environmentally acceptable -
Social and cultural significance - Public interest
Legislation:
Aboriginal Heritage Act 1972 (WA)
Environmental Protection Act 1986 (WA), Sch 5, cl 2
Rights in Water and Irrigation Act 1914 (WA), s 2, s 2(1), s 3, s 3(1), s 3(1)(c),
s 3(2)(c), s 4(1), s 4(1)(a)(i), s 4(2), s 4(3), s 5A, s 5C, s 5C(1)(c), s 5C(1)(d),
s 5C(3), s 5D, s 6(3), s 20, s 20(1), s 20(1)(c), s 26GG(1)(d), Sch 1, cl 1, cl 4(1),
cl 4(3), cl 6(1), cl 6(2), cl 6(4), cl 7(2), cl 7(2)(a), cl 7(2)(b), cl 7(2)(c),
cl 7(2)(d), cl 7(2)(e), cl 7(2)(f), cl 7(2)(g), cl 7(2)(g)(iv), cl 7(2)(h), cl 8, cl 15,
cl 15(2), Pt III, Div 2, Div 3D, Appendix, item 2
State Administrative Tribunal Act 2004 (WA), s 27(1), s 27(2), s 28, s 29(3),
s 32(2)(b)
Result:
Application allowed in part
Respondent's decision varied
Category: B
Representation:
Counsel:
Applicant : Mr P Fletcher
Respondent : Mr E Heywood & Ms E Wignell
Solicitors:
Applicant : McWilliams Davis Lawyers
Respondent : State Solicitor's Office
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Case(s) referred to in decision(s):
Clive Elliott Jennings & Co Pty Ltd v Western Australian Planning Commission
[2002] WASCA 276; (2002) 122 LGERA 433
Crossley v English [2025] WASCA 141
Crossley v English [No.2] [2024] WASC 268
ICM Agriculture Pty Ltd v The Commonwealth [2009] HCA 51;
(2009) 240 CLR 140
More and Water and Rivers Commission [2006] WASAT 112
Ord Irrigation Co-Operative Limited and Department of Water and
Environmental Regulation [2020] WASAT 68
Ord Irrigation Cooperative Ltd v Department of Water [2018] WASCA 83
Prestidge and Department of Water and Environmental Regulation
[2023] WASAT 9
Re Drake and Minister for Immigration and Ethnic Affairs (No 2) (1979) 2 ALD
Tah Land Pty Ltd v Western Australian Planning Commission
[2009] WASC 196
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[2026] WASAT 76
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REASONS FOR DECISION OF THE TRIBUNAL:
Introduction
1 On 13 September 2023, the Minister for Water (Minister) granted
to the applicant, Quininup Holdings Pty Ltd (applicant), a licence to
take surface water pursuant to s 5C of the Rights in Water and
Irrigation Act 1914 (WA) (Current Licence) (RIWI Act).
The delegate of the Minister, and the respondent in this proceeding, is
the Program Manager South West Region (respondent).
2 A farm dam, which is an authorised activity under the Current
Licence, is located on the applicant's property in Wilyabrup (Lot 131
Dam). The Lot 131 Dam is filled by the diversion of surface water
from Quininup Brook (Quininup Brook or watercourse) via pumping
from a downstream dam located on the tributaries of Quininup Brook
(Lot 14 Dam).
3 The Current Licence enables the taking of an Annual Water
Entitlement (AWE) of 17,500 kilolitres and was granted subject
to conditions.
4 On 30 September 2023, pursuant to s 26GG(1)(d) of the
RIWI Act, the applicant commenced a proceeding in the Tribunal
seeking a review of two of the four conditions imposed on the Current
Licence. The first condition, subject to review, only permits the
applicant to take water from the watercourse to fill the Lot 14 Dam
during the winter take period between 1 June and 30 September, or as
otherwise directed by the Department of Water and Environmental
Regulation (Department) (WTP Condition). The second condition,
subject to review, requires the applicant to bypass all flows in the
watercourse between 1 October and 31 May next (Bypass Condition).
The applicant seeks orders from the Tribunal that the two conditions
should be set aside.
5 The Tribunal must review the respondent's decision by way of a
hearing de novo for the purposes of producing the correct and
preferable decision based on the material at the time of the review.1
The Tribunal is to act according to equity, good conscience, and the
substantial merits of the case without regard to technicalities and legal
forms.2 Section 29(3) of the State Administrative Tribunal Act 2004
(WA) (SAT Act) confers specific power on the Tribunal to make any
1 State Administrative Tribunal Act 2004 (WA) (SAT Act), s 27(1) and s 27(2).
2 SAT Act, s 32(2)(b).
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order that it considers appropriate, including an order to affirm, vary or
set aside the respondent's decision.
6 For the reasons that follow, we have concluded that the correct and
preferable decision is to allow the review application in part and vary
the respondent's decision to impose the WTP Condition and
Bypass Condition by modifying the winter take period.
Issues for determination
7 The Tribunal must determine whether the correct and preferable
decision is to impose the WTP Condition and/or the Bypass Condition
on the Current Licence and, if so, what should be the terms of the
condition(s).
Factual background
8 There were certain factual matters that were not in dispute
between the parties. We make the findings set out in this paragraph in
relation to those matters.
(1) The applicant is the registered proprietor of Lot 131
Caves Road, Wilyabrup, formally known as Lot 131 on
Plan 25420, Volume 2519 Folio 600 (Lot 131).3
(2) Cape Falls Pty Ltd is the registered proprietor of Lot 14 Caves
Road, Wilyabrup, formally known as Lot 14 on Diagram 68610,
Volume 1705 Folio 117 (Lot 14).4
(3) Lot 14 is located to the east of Lot 131.
(4) On 24 January 2013, the applicant made an application for a
licence pursuant to s 5C of the RIWI Act to take surface water
from Lot 14.5
(5) On 12 July 2013, the Minister granted a licence to the applicant
to take surface water, which was issued under Instrument
No. SWL177061(1) (First Licence).6
3 Respondent's Statement of Issues, Facts and Contentions filed on 19 September 2024 (Respondent's
SIFC), para 1; Applicant's Statements of Issues Facts and Contentions filed on 10 October 2025
(Applicant's SIFC), page 1.
4 Respondent's SIFC, para 2; Applicant's SIFC, page 1.
5 Respondent's SIFC, para 3; Applicant's SIFC, page 1; Respondent's s 24 Bundle, filed on 19 September
2024 (Exhibit 1) (Respondent's Bundle), page 15.
6 Respondent's SIFC, para 4; Applicant's SIFC, page 1; Respondent's Bundle, page 15.
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(6) The First Licence had an AWE of 17,500 kilolitres.7
It specified the location of the water source to be Lot 14 and
permitted the diversion and storage of surface water from
Lot 14 to Lot 131, respectively.8
(7) The First Licence was issued subject to two conditions,
namely:9
(a) the annual water year for water taken under the licence
is defined as 1 July to 30 June next; and
(b) the licensee is to provide a completed 'Water Use
Return' to the Department of Water by 31 July each
year.
(8) The First Licence was valid for a ten-year period and,
consequently, had an expiry date of 1 July 2023.10
(9) The applicant applied to renew the First Licence on
28 July 2023.11 The application was made after the
First Licence had expired.12 Consequently, the Department
treated the application for renewal as an application for a new
licence under s 5C of the RIWI Act.13
(10) On 13 September 2023, the respondent granted the applicant a
new licence to take surface water under Instrument
No. SWL209115(1) which has an AWE of 17,500 kilolitres
(or Current Licence).14
(11) The location of the water source specified on the Current
Licence is Lot 14.15 The Current Licence permits the diversion
and storage of surface water from Lot 14 to Lot 131,
respectively.16
7 Respondent's SIFC, para 5; Applicant's SIFC, page 1; ts 194 - 195, 10 December 2025; Witness Statement
of Owen Bennett filed on 31 October 2025 (Exhibit 4) (Mr Bennett's statement) paras 58 - 61;
Respondent's Bundle, page 15.
8 Respondent's SIFC, para 5; Applicant's SIFC, page 1; Respondent's Bundle, page 15.
9 Respondent's SIFC, para 6; Applicant's SIFC, page 1; Respondent's Bundle, page 15.
10 Respondent's SIFC, para 7; Applicant's SIFC, page 1; Respondent's Bundle, page 15.
11 Respondent's SIFC, para 9; Applicant's SIFC, page 1; Respondent's Bundle, page 16.
12 Respondent's SIFC, para 10; Applicant's SIFC, page 1; Respondent's Bundle, page 16.
13 Respondent's SIFC, para 10; Applicant's SIFC, page 1; Respondent's Bundle, page 16.
14 Respondent's SIFC, para 11; Applicant's SIFC, page 1; Respondent's Bundle, page 25.
15 Respondent's SIFC, para 12; Applicant's SIFC, page 1; Respondent's Bundle, page 25.
16 Respondent's SIFC, para 12; Applicant's SIFC, page 1; Respondent's Bundle, page 25.
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(12) The Current Licence was issued subject to four conditions,
namely:17
(a) the annual water year for water taken under the licence
is defined as 1 July to 30 June (Condition 1);
(b) the licensee must not, in any water year, take more water
than the AWE specified in the licence (Condition 2);
(c) the licensee shall only take water from watercourse to
fill the dam between 1 June and 30 September, or as
otherwise directed by the Department (or
WTP Condition); and
(d) the licensee shall bypass all flows in the watercourse
between 1 October and 31 May next (or
Bypass Condition).
(13) Conditions 1 and 2 are not in dispute in this proceeding.18
The conduct of the hearing and witness evidence
9 The applicant relied on the evidence of Mr Chistopher Mulcahy,
who is a director of SW Hydrology. Mr Mulcahy gave evidence in
respect of matters relating to hydrology, geomorphology and ecology.
He holds a Bachelor of Environmental Science degree (with honours)
from the University of Notre Dame and the University of Western
Australia. Mr Mulcahy prepared a witness statement dated 3 November
2025 which he adopted as his evidence-in-chief and was
cross-examined.
10 Mr Brettney Fogarty, who is a director of the applicant and Cape
Falls Pty Ltd, prepared a witness statement dated 3 November 2025
which he adopted as his evidence-in-chief and was cross-examined.
11 The respondent relied on the evidence of the following witnesses:
(1) Dr Phillip Jordan, a principal hydrologist with HARC Services
Pty Ltd. Dr Jordan holds a Bachelor of Engineering
(with honours) in civil engineering from the University of
Queensland and a Doctor of Philosophy in hydrology from
Monash University. He provided evidence in respect of matters
relating to hydrology, including catchment modelling to
17 Respondent's SIFC, para 13; Applicant's SIFC, page 1; Respondent's Bundle, page 25.
18 Respondent's SIFC, para 14; Applicant's SIFC, page 1; Respondent's Bundle, page 25.
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[2026] WASAT 76
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simulate streamflow on Lot 14. Dr Jordan prepared a witness
statement dated 28 October 2025 which he adopted as his
evidence-in-chief and was cross-examined.
(2) Mr Adam Green, Principal Water Planner, Water Allocation
Planning at the Department. Mr Green gave evidence in respect
of matters relating to ecohydrology, riverine ecology and
geomorphology. He holds a Bachelor of Science degree
(with honours) in natural resource management from the
University of Western Australia. Mr Green prepared a witness
statement dated 31 October 2025 which he adopted as his
evidence-in-chief and was cross-examined.
(3) Mr Owen Bennett, Acting District Manager of the Geographe
Capes District at the Department. Mr Bennett undertakes
delegated decision-making on applications for licences to take
water under the RIWI Act and determined the application for
the Current Licence. He holds a Bachelor of Social Science
degree in environmental management from Edith Cowan
University. Mr Bennett prepared a witness statement dated
30 October 2025 which he adopted as his evidence-in-chief and
was cross-examined.
12 Following a chaired expert conferral held on 28 November 2025,
Mr Mulcahy, Dr Jordan and Mr Green prepared a joint statement dated
5 December 2025 relating to matters of hydrology within their
knowledge and expertise. At the final hearing, those witnesses gave
their evidence concurrently.
13 The Tribunal had the benefit of a site view on 8 December 2025
which was attended by the parties and their legal counsel.
The locations visited during the site view included the banks and
western edge of the Lot 14 Dam, the Lot 14 dam wall and spillway,
and the tributaries that flow into the Lot 14 Dam. The Tribunal also
viewed the applicant's monitoring sites, including the location of two
v-notch weirs upstream and downstream of the Lot 14 Dam, as well as
the Quininup Brook main channel and its confluence downstream of the
Lot 14 Dam.
The statutory framework
14 We will next outline the statutory framework under the RIWI Act
that applies to licensing decisions by the Minister, including the
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[2026] WASAT 76
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Minister's power (and the power of the Tribunal on review) to grant or
refuse a licence and impose licence conditions.
The statutory requirement for a licence to take water
15 The management, use and protection of water resources across the
State is regulated by the provisions of the RIWI Act. The right to
the use and control of water in any watercourse, wetland or
underground water source is vested in the Crown except as allocated
under the RIWI Act or another written law.19
16 Relevantly, a 'watercourse' is defined in s 3(1) of the RIWI Act to
mean any river, creek, stream or brook in which water flows, and any
collection of water (including a reservoir) into, through, or out of which
those surface waters flow. The definition extends to any place where
water flows that is prescribed to be a watercourse.20 It is immaterial
that a watercourse has been diverted from its natural course or may
have been artificially improved or altered.21
17 Pt III of the RIWI Act provides for the ownership and control of
water resources in the State. It is an offence to take water from any
watercourse except under, and in accordance with, a licence granted by
the Minister under s 5C(1)(d) of the RIWI Act (s 5C licence), or a right
conferred by the RIWI Act or another written law.22
18 The word 'take' is defined in s 2(1) of the RIWI Act as follows:
take, in relation to water, means to remove water from, or reduce the
flow of water in, a watercourse, wetland or underground water source,
including by -
(a) pumping or siphoning water; or
(b) stopping, impeding or diverting the flow of water; or
(c) releasing water from a wetland; or
(d) permitting water to flow under natural pressure from a well; or
(e) permitting stock to drink from a watercourse or wetland,
19 RIWI Act, s 5A. The right to take and divert water cannot be established by length of time of use, or
otherwise, except in accordance with the RIWI Act or any other written law: RIWI Act, s 5D.
20 RIWI Act, s 3(1)(c).
21 RIWI Act, s 3(2)(c).
22 RIWI Act, s 5C(1)(c).
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and includes storing water during, or ancillary to, any of those
processes or activities[.]
19 The Minister, and other persons performing functions under Pt III
of the RIWI Act, must seek to ensure that the objects listed in s 4(1) of
the RIWI Act are achieved23 including a decision whether to grant or
refuse a 5C licence and, if granted, the terms, conditions and
restrictions to be included in the 5C licence. Section 4(1) of the
RIWI Act provides:
(1) The objects of this Part are -
(a) to provide for the management of water resources, and
in particular -
(i) for their sustainable use and development to
meet the needs of current and future users; and
(ii) for the protection of their ecosystems and the
environment in which water resources are
situated, including by the regulation of
activities detrimental to them;
and
(b) to promote the orderly, equitable and efficient use of
water resources; and
(c) to foster consultation with members of local
communities in the local administration of this Part,
and to enable them to participate in that administration;
and
(d) to assist the integration of the management of water
resources with the management of other natural
resources.
20 The expression 'use and development' in subsection 4(1)(a)(i) is
defined in s 4(2) of the RIWI Act to include the use and development
for domestic, commercial, recreational, cultural and navigational
purposes.
21 Section 5C(3) of the RIWI Act provides that Sch 1 to the
RIWI Act has effect to make provision for a 5C licence.
23 RIWI Act, s 4(3).
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The Minister's power to grant a s 5C licence subject to conditions
22 Division 2 of Sch 1 to the RIWI Act governs the grant or refusal of
a 5C licence. Where the Minister proposes to refuse an application for
a 5C licence or to grant a 5C licence subject to the inclusion of a term,
condition or restriction that the Minister considers is inconsistent with
the terms of the application, the applicant must be afforded an
opportunity to make written submissions in respect of the proposed
decision.24 The Minister must have regard to any submissions made
before making a final decision.25
23 The matters to which licence terms, conditions or restrictions may
relate are contained in the Appendix to Sch 1 to the RIWI Act and,
relevantly, include the use, management, protection and enhancement
of any water resource and its ecosystem, or the environment in which
the water resource is situated.26
24 At the Minister's discretion, the Minister may include any term,
condition or restriction on the grant of a s 5C licence.27 In exercising
that discretion, the Minister is to have regard to all matters that the
Minister considers relevant, including the mandatory relevant
considerations identified in cl 7(2)(a)-(h) of Sch 1 to the RIWI Act.28
25 Clause 7(2) of Sch 1 to the RIWI Act provides:
(2) In exercising that discretion, the Minister is to have regard to all
matters that the Minister considers relevant, including whether
the proposed taking and use of water -
(a) are in the public interest; or
(b) are ecologically sustainable; or
(c) are environmentally acceptable; or
(d) may prejudice other current and future needs for water;
or
(e) would, in the opinion of the Minister, have a
detrimental effect on another person; or
24 RIWI Act, cl 6(1) - 6(2) of Sch 1.
25 RIWI Act, cl 6(4) of Sch 1.
26 RIWI Act, Appendix to Sch 1, item 2.
27 RIWI Act, cl 15(2) of Sch 1.
28 RIWI Act, cl 15(2) of Sch 1. Ord Irrigation Cooperative Ltd v Department of Water [2018] WASCA 83
at [66]; Ord Irrigation Co-Operative Limited and Department of Water and Environmental Regulation
[2020] WASAT 68 at [96].
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(f) could be provided for by another source; or
(g) are in keeping with -
(i) local practices; or
(ii) a relevant local by-law; or
(iii) a plan approved under Part III Division 3D
Subdivision 2; or
(iv) relevant previous decisions of the Minister;
or
(h) are consistent with -
(i) land use planning instruments; or
(ii) the requirements and policies of other
government agencies; or
(iii) any intergovernmental agreement or
arrangement.
26 The Minister must refuse to grant a 5C licence if the Minister
considers that the person would not be willing or able to comply with
any terms, conditions or restrictions.29
27 We will next consider the geomorphological, hydrological and
cultural attributes of the Quininup Brook catchment in which the Lot 14
Dam, the subject of a s 5C licence (the Current Licence), is located.
The Quininup Brook catchment
28 Located in the Leeuwin Naturalist National Park, downstream of
Lot 14, is Quininup Falls which is highly seasonal. Quininup Falls is a
recreational and tourist attraction with social and cultural values in both
the Falls and the area surrounding it, including the Cape to Cape
walking track.30 Within the vicinity of Quininup Falls, there are two
sites registered under the Aboriginal Heritage Act 1972 (WA) which
include reaches of Quininup Brook.31
29 RIWI Act, Sch 1, cl 8.
30 Mr Bennett's statement, paras 183 - 184 and 188; ts 329, 11 December 2025.
31 Mr Bennett's statement, paras 185 - 187, OB6 and OB7; ts 329, 11 December 2025.
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29 The Leeuwin Naturaliste Ridge is Orthoclasic and Plagioclasic
granite. The granite underlies the entire Quininup Brook catchment,
which is overlain with colluvium and alluvium deposits in the valleys.32
30 The soils of the Quininup Brook catchment are not uniform.33
The portion of the catchment to the west of the Lot 14 Dam has
sand/limestone deposits of marine origin overlying granite.34
The eastern catchment contains gravel loams and duplex soils with
interspersed sand veins. Clay loams are found within valleys to the
west of Caves Road, along the main channel of Quininup Brook, with
coastal dunes and limestone present closer to the coast.35 To the south
of the Lot 14 Dam, the catchment has perched water tables where sand
deposits overlay clay and granite.36 There is an exposed granite ridge
known as 'Moses Rock' which generates runoff towards the central
tributary feeding the Lot 14 Dam.37
31 Stream gauging station 610063 is located on the main channel of
the eastern Quininup Brook catchment and measures volumetric flow
(streamflow gauge).38 The streamflow gauge was operational between
27 May 2015 and 26 April 2022 but had missing data between
12 August 2020 and 31 May 2021, which may have been caused by a
malfunction in the recording equipment several months earlier.39
32 In the Quininup Brook catchment, there is high variability when
flows cease in different streams and different stream reaches within
different stream catchments, due to variations in catchment size,
topography, vegetation, soils and geology.40 Streamflow in a
rainfall-runoff driven catchment, without headwater springs and
gaining and losing reaches (stream lengths that gain flow from or lose
flow to groundwater), would cease earlier in the year higher in the
catchment.41
32 Joint statement of expert witnesses filed on 5 December 2025, (Exhibit 6) (Joint Statement),
pages 13 - 14.
33 ts 81 - 82, 9 December 2025; ts 117 - 119, 10 December 2025.
34 Joint Statement, pages 13 - 14.
35 Joint Statement, pages 13 - 14.
36 Joint Statement, pages 13 - 14.
37 Joint Statement, pages 13 - 14.
38 Expert opinion report of Dr Phillip Jordan dated 28 October 2025 (Exhibit 5) (Dr Jordan's expert
report), pages 3 - 4; Figure 5-1.
39 Expert report of Dr Jordan, page 3.
40 Joint Statement, page 4.
41 Joint Statement, page 18.
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Page 14
33 The reach of Quininup Brook just upstream of the Quininup Falls
and below the Lot 14 Dam is likely to be perennial.42 Reaches of
Quininup Brook further upstream, including the catchment upstream of
the Lot 14 Dam are unlikely to be perennial.43 Quininup Brook
upstream of the streamflow gauge, for example, typically ceases to flow
between December and May when the groundwater table falls below
the base level of the river channel.44
Tribunal's consideration
34 Section 6(3) of the RIWI Act provides for the proclamation of
surface water areas so that surface water within a proclaimed area is
surface water to which the RIWI Act applies. On 21 September 2007,
the Cape to Cape North, Cape to Cape South, Lower Blackwood River
and Geographe Bay Rivers surface water areas in the South West were
proclaimed under the RIWI Act.45 There was no dispute that the
Quininup Brook catchment area is within the Cape to Cape North
Surface Water Area and is surface water to which s 5C of the RIWI Act
applies.46
35 The Cape to Cape North Surface Water Area is within the
Whicher Area for the purpose of the Department's management and
allocation of surface water (Whicher Area). The Whicher Area is
divided into three sections, namely, Capel River, Busselton Coast and
Lower Blackwood. These subsections are further divided into subareas
for hydrological and allocation planning purposes. One of those
subareas is Quininup, which is within the Busselton Coast, and the
proclaimed Cape to Cape North Surface Water Area
(Quininup subarea).47
36 The parties agreed that Lot 14 and Lot 131 are located within the
Quininup subarea of the Whicher Area for the purpose of surface water
allocation.48
Whicher Area Surface Water Allocation Plan
37 The main policy framework for the allocation of surface water in
the Whicher Area is the Whicher Area Surface Water Allocation Plan
42 Joint Statement, page 4.
43 Joint Statement, page 4.
44 Witness statement of Adam Green, filed on 31 October 2025 (Exhibit 3) (Mr Green's statement), para 58.
45 Respondent's SIFC, para 19; Applicant's SIFC, page 1; Respondent's Bundle, page 829.
46 Respondent's SIFC, para 19; Applicant's SIFC, page 1; Respondent's Bundle, page 829.
47 Respondent's SIFC, para 20; Applicant's SIFC, page 1; Respondent's Bundle, pages 63, 91 - 95.
48 Respondent's SIFC, para 21; Applicant's SIFC, page 1.
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(Whicher Allocation Plan). The purpose of the Whicher Allocation
Plan is to provide the Department with direction on how surface water
resources in the Whicher Area will be allocated, and actively managed
through licensing, to provide greater security for water users and the
environment.49
38 There are a number of objectives for managing surface water in
the Whicher Area which are set out in cl 3.1 of the Whicher Allocation
Plan as follows:
• minimise impacts of new surface water developments on
existing water users
• protect key ecological, cultural and social values so they are
kept at an acceptable level of risk from the effects of surface
water use
• manage commercial use in proclaimed areas through licensing
• provide regular statements against the management objectives
outlined in this plan and update the community on the ongoing
work to review this plan
• implement effective water management through measurement,
monitoring, auditing, compliance and reporting to provide
transparency and accountability of water use.
39 The relevant subarea in this proceeding, shown in Figure 11 of the
Whicher Allocation Plan, is the Quininup subarea, which is fully
allocated.50
40 The Whicher Allocation Plan sets out, in Table 4, allocation and
licensing policies which apply to the Whicher Area (and Quininup
subarea), including as follows:
(1) Clause 3.3.1 provides that the Department may, at its discretion,
include in a licence any terms, conditions or restrictions as
stated in Sch 1, cl 15 of the RIWI Act.51
(2) Clause 3.3.2 provides that licence conditions may state when
flows must be bypassed during the year.52
49 Respondent's Bundle, page 59.
50 Respondent's SIFC, para 52; Applicant's SIFC, page 3; Respondent's Bundle, pages 95 - 96.
51 Respondent's SIFC, para 54; Applicant's SIFC, page 3; Respondent's Bundle, page 102.
52 Respondent's SIFC, para 54; Applicant's SIFC, page 3; Respondent's Bundle, page 102.
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(3) Clause 5 provides that allocation and licensing decisions for the
Whicher Allocation Plan will take into account a relatively drier
climate period, based on rainfall data from the period
1975 - 2005.53
(4) Clause 6.1.4 provides, relevantly, that the Department:54
may require existing on-stream dams to have a bypass system
to control flows, as well as other controls that allow for the
migration of aquatic species. The [D]epartment will
implement this policy as required, which is consistent with the
[D]epartment's Statewide policy no. 5 - Environmental water
provisions policy (WRC 2000b) on providing water for
environmental flows and passage of aquatic life.
(5) Clause 6.1.5 provides that:55
The [D]epartment is unlikely to approve new applications to
take surface water (including direct pumping) from a
watercourse during periods of low flow (generally in summer),
due to the ecological needs of the system during that time.
41 Whilst a draft version of the Whicher Allocation Plan was subject
to public comment,56 it is not a statutory management plan because it
was not approved under Pt III Div 3D of the RIWI Act. Consequently,
it is not a statement of government policy to which we must have
regard for the purposes of s 28 of the SAT Act. Nevertheless, the
Whicher Allocation Plan informed the respondent's decision to impose
the WTP Condition and Bypass Condition and, consequently, is a
policy that is relevant to our determination.
42 We will next consider the manner in which surface water is
diverted from the watercourse on Lot 14 to Lot 131.
Diversion of water from Lot 14 to Lot 131
43 The Lot 14 Dam is constructed over a natural low point in the
landscape where three tributaries of Quininup Brook converge.
53 Respondent's Bundle, page 102.
54 Respondent's Bundle, page 103.
55 Respondent's Bundle, page 103.
56 Respondent's Bundle, page 65.
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These tributaries meet at confluences to the south, south-east and east57
of the Lot 14 Dam.58
44 There is also a smaller dam located on the main channel of
Quininup Brook (Riparian Dam or QB Dam) that is generally not
regarded as being the subject of the Current Licence, or of any licence
to take surface water on the basis that the surface water in the Riparian
Dam or QB Dam would only be taken for riparian uses.59
45 The applicant pumps water from the Lot 14 Dam to the Lot 131
Dam.60 The Lot 131 Dam is used by the applicant on Lot 131 for
irrigation and, when necessary, firefighting.61 The Lot 131 Dam is not
licenced under the RIWI Act.62 A plan showing the location of Lot 14
and Lot 131 and the tributaries intercepted by the Lot 14 Dam is
Annexure A to these reasons.
46 The applicant contends that the decision to impose the
WTP Condition and the Bypass Condition was based on the application
of policy with no, or insufficient, consideration of the specific
circumstances of the Lot 14 Dam and the Quininup subarea.63
The applicant further contends that a sump and pipe bypass for the
Lot 14 Dam would require ongoing maintenance, operate inefficiently
and be expensive to install.64 In contrast, it is the respondent's position
that without the WTP Condition and Bypass Condition, transitional
flows will be impeded by the Lot 14 Dam and, consequently, both
conditions are necessary to protect the downstream water-dependent
social, cultural and environmental values of Quininup Brook.65
47 We will next consider the unique hydrological features of the
Lot 14 Dam.
57 The tributary to the east of the Lot 14 Dam is also referred to in the proceeding as the north-east channel or
the northern most tributary: see Joint Statement, page 8; ts 22, 9 December 2025.
58 Respondent's SIFC, para 23; ts 22, 9 December 2025.
59 Respondent's SIFC, para 21; Applicant's SIFC, page 1.
60 Witness statement of Brettney Fogarty (Exhibit 7) (Mr Fogarty's statement), para 9;
ts 22, 9 December 2025.
61 Mr Fogarty's statement, para 60.
62 Mr Bennett's statement, para 53; Respondent's SIFC, para 99; Applicant's SIFC, page 6.
63 Applicant's opening submissions filed on 3 December 2025, para 9.
64 Applicant's closing submissions filed on 3 March 2026, (Applicant's closing submissions) D7;
Mr Fogarty's statement, paras 33 - 34.
65 Respondent's closing submissions filed on 3 March 2026, (Respondent's closing submissions), para 44.
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The hydrological features of the Lot 14 Dam
48 The Lot 14 Dam has been in place for over 40 years.66
It intercepts water from three tributaries of Quininup Brook. The water
is held back in part by a leaky earthen wall, located at the northern end
of the reservoir, and in part by a naturally occurring porous sand
barrier.67 The Lot 14 Dam is a fill and spill dam. Once its capacity is
reached (at the end of winter), the Lot 14 Dam loses water down a
lower section that acts as a spillway, located at the eastern end of the
dam wall (spillway).68 According to Mr Fogarty, the Lot 14 Dam has
overflowed every year since his company purchased Lot 14.69 Spills
from the Lot 14 Dam flow along an unnamed tributary of Quininup
Brook for a distance of approximately 100 metres before entering the
main channel of Quininup Brook.70
49 There was no dispute that the Lot 14 Dam is the last farm dam
before Quininup Falls. Due to the location of the Lot 14 Dam, the
respondent contends that downstream flows outside the winter take
period, and during the transitional or 'shoulder period', are particularly
important to the social and cultural values of the Falls.71
50 To measure stream flow at the Lot 14 Dam, the applicant installed
two 90 degree v-notch weirs (V-notch). Measurements of depth of
flow at the first V-notch provided for calculation of the rate
of volumetric flow, in litres per second, entering the Lot 14 Dam
(site A) and, at the second V-Notch, provided for calculation of the
volume of water leaking from the dam (site B).72 Based on
Mr Mulcahy's measurements taken at site A and site B on 28 October
2025 (10 days after flow ceased at the spillway), the applicant says that
726 kilolitres per day flow directly below the Lot 14 Dam.73
51 Mr Mulcahy also monitored the rate of flow at two open channels,
namely site C (downstream of the Riparian Dam) and site
D (downstream of the Lot 14 Dam).74
66 Witness statement of Christopher Mulcahy filed on 13 November 2025, (Exhibit 8) (Mr Mulcahy's expert
report), page 8.
67 ts 352 - 53, 19 March 2026.
68 Dr Jordan's expert report, page 64.
69 ts 306 - 307, 11 December 2025.
70 Dr Jordan's expert report, page 64.
71 Respondent's SIFC, paras 61 and 87.
72 Mr Mulcahy's expert report, page 3; Exhibit 14 and Exhibit 15.
73 Applicant's closing submissions, para B3, B6.
74 Mr Mulcahy's expert report, page 5; Exhibit 14 and Exhibit 15.
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52 The joint experts agreed, and we find, that Lot 14 Dam has a
surveyed volume of 112.48 million litres or 112.48 megalitres.75 Based
on this volume, at the point in time of cessation of spill, the applicant
estimates that the volume lost to evaporation is approximately
36 megalitres.76 The applicant says it pumps approximately
12 megalitres per year from the Lot 14 Dam and that, according to
Mr Fogarty, approximately 5 megalitres remains in the dam at the end
of February which is unable to be released by seepage.77 Based on
these figures, the applicant calculated that from October to February,
more than 50 megalitres are progressively discharged into Quininup
Brook from the Lot 14 Dam by seepage.78
53 Relying on a rate of flow of approximately 700 kilolitres per day,
it is the applicant's position that it would take 71 days from the
cessation of flow at the spillway (usually in September each year) to
discharge 50 megalitres.79
54 Consequently, the applicant contends that the Lot 14 Dam
delivers, by continuous seepage, a substantial volume of water for the
benefit of the downstream environment throughout much of the dry
months of the year.80 The applicant further contends that this includes
the period of cessation of flow in the northern tributary of Quininup
Brook which, according to gauge data, occurs in mid-November in
most years.81
Findings
55 Based on the evidence of the joint experts, we find that the
catchment area of the Lot 14 Dam is approximately 7.6 km².82
The catchment area of the streamflow gauge is approximately 10 km²
and that the total catchment area of Quininup Brook to Quininup Falls
is approximately 18.5 km².
56 The joint experts agreed, and we find, that there is considerable
variability in the amount and timing of both rainfall and potential
75 Joint Statement, page 3; Exhibit 20.
76 Applicant's closing submissions, para B1.
77 Applicant's closing submissions, para B2.
78 Applicant's closing submissions, para B1; para 12.4(h); ts 355, 19 March 2026.
79 Applicant's closing submissions, para B4; ts 358, 19 March 2026.
80 Applicant's closing submissions, para B7.
81 Applicant's closing submissions, para B7.
82 Joint Statement, page 3.
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evapotranspiration, which causes year to year variations in the volume
and timing of inflows to the Lot 14 Dam.83
57 We further find, based on the evidence of the joint experts, that the
flows recorded at V-notch weir sites A and B and estimated at open
channel sites C and D represent a 'snapshot in time' of flows on the
monitored days and are subject to certain limitations and assumptions.84
Mr Mulcahy acknowledged, for example, that the upstream pool area
had not been accurately surveyed.85
58 We are unable to rely on the applicant's calculations for the
purposes of determining the leakage rate of the Lot 14 Dam or the
length of time that the seepage continues after the cessation of flow
from the spillway. Whilst we accept that certain losses to Quininup
Brook occur as a result seepage through the dam wall and from
evapotranspiration, it is also possible that the Lot 14 Dam loses water
via other pathways, including by infiltration to contribute to the
recharge of local groundwater aquifers.
59 Moreover, the joint experts agreed, and we find, that the recorded
flows at site A and B is a 'snapshot in time' and, consequently, we
cannot be satisfied that the measurements accurately depict the leakage
rates through the wall of the Lot 14 Dam. The joint experts agreed, and
we find, that it is not possible to determine how the leakage rate would
change with the depth of water stored in the Lot 14 Dam without
additional data.86 We find, based on the evidence of the joint experts,
that the leakage rates from Lot 14 Dam would reduce as the depth of
the water stored in it fell (due to reduced head and pressure) and that, at
some point in time, water would stop seeping from the dam.87
The applicant's calculations did not account for the reduction in head
height and leakage rates over time and, consequently, we are unable to
accept its position that more than 50 megalitres is discharged from the
Lot 14 Dam wall by seepage each year.
60 We will next consider the impact that farm dams may have on
water-dependent ecosystems, such as the Quininup Brook catchment.
83 Joint Statement, page 4; ts 80, 9 December 2025.
84 Joint Statement, page 3.
85 Mr Mulcahy's expert report, page 4.
86 Joint Statement, page 3.
87 Joint Statement, page 3.
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The impact of farm dams on riverine ecology
61 The water-dependent ecological values of a stream include those
parts of the ecosystem that rely on the presence of water, including any
aquatic or semi-aquatic flora and fauna.88 There was no dispute, and
we find, that the environment downstream from the Lot 14 Dam is a
water-dependent ecosystem.
62 The ecological water requirement (EWR) of a stream is a key
consideration in water resource management decisions, including the
sustainable level of farm dam development and water licensing
strategies.89 Mr Green described the EWR of a stream, also known as
environmental flow, as the minimum flow needed to maintain its
associated values of water-dependent ecosystems at a low level of
risk.90 In Mr Green's opinion, a flow regime that meets the EWR of a
stream will 'often also meets its social and cultural values'.91
63 It is the applicant's position that there is insufficient data to
determine an EWR for Quininup Brook. It observed that the only
available stream flow data for Quininup Brook is from a faulty gauge
(the streamflow gauge) which produced six years of data until it was
discontinued in 2021.92
64 Whilst no EWR studies have been conducted within the Quininup
Brook catchment, Mr Green referred to studies that had been completed
in the nearby Wilyabrup Brook and Cowaramup Brook catchments.93
In Mr Green's opinion, these studies can be relied on to provide an
understanding of flow rate and ecological function for streams in the
Leeuwin-Naturaliste region, which includes Quininup Brook.94
Mr Green expected there to be similar rainfall-runoff patterns between
the Cowaramup Brook catchment and the Quininup Brook catchment
(due to their comparable size) which, in his opinion, can be used to
inform water resource management decisions, including how surface
water can be taken from Quininup Brook at a low risk to existing
water-dependent ecological values.95
88 Mr Green's statement, para 39.
89 Mr Green's statement, para 38.
90 Mr Green's statement, para 35.
91 Mr Green's statement, paras 29 and 154.
92 Applicant's closing submissions, paras E2 and E3.
93 Mr Green's statement, paras 119 - 120.
94 Mr Green's statement, paras 121 - 122; Figure 1.
95 Mr Green's statement, paras 121 - 122; Figure 1.
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65 Mr Green described the highly seasonal flow regime of streams in
the South West, including Quininup Brook, and its relationship to
aquatic species, as follows:96
The annual pattern of summer (dry season) drought and winter
(wet season) flood is a key feature of rivers in the South West (Kennard
et al. 2010). This sequence of a wet season followed by a dry season
during which flow may cease, is a fundamental pattern in South West
streams. It has been shown to have a strong influence on the
morphology of aquatic species (e.g. their size, appearance, structure
etc), their life-history strategies (e.g. how they move, eat, breed etc),
and variations in their abundance and diversity.
66 It was not in contest that on-stream dams modify the downstream
flow regime which can present a risk to the water-dependent riverine
ecology, particularly in low flow years and due to the effects of climate
change.97 In Mr Green's opinion, on-stream dams can have a
significant impact on dry season low flows, early season 'freshes' and
late season recessional flows.98 He explained that, at the start of the
flow season, on-stream dams capture flow while they are filling which
prevents water passing downstream until the dams fill and spill.99
Mr Green referred to the importance of early season 'freshes' as
follows:100
Early-season flows relieve stress in river pools and areas of permanent
water (the stresses for the species being high temperatures and low
dissolved oxygen), provide cues for breeding migrations of native fish,
and provide habitat for microcrustaceans, aquatic insects, waterbirds,
and the larval stages of some terrestrial insects.
67 The Western pygmy perch (Edelia vittata)101 and the Gilgie
(Cherax quinquecarinatus)102 were found in Quininup Brook near the
base of Quininup Falls when sampling was performed by the
Department in February 2024.103 Mr Green said it is likely that aquatic
fauna species present in the Quininup Brook catchment also include
Western minnow (Galaxias occidentalis),104 Western mud minnow
96 Mr Green's statement, paras 29, 42 and 117.
97 Mr Green's statement, para 31.
98 Mr Green's statement, paras 46, 159 - 160.
99 Mr Green's statement, para 90.
100 Mr Green's statement, para 53.
101 Mr Green's statement, paras 123 - 124.
102 Mr Green's statement, paras 140 - 141.
103 Mr Green's statement, paras 144 - 148.
104 Mr Green's statement, paras 123 - 124.
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(Galaxiella munda),105 Nightfish (Bostockia porosa),106 and Carter's
freshwater mussel (Westralunio carteri).107
68 The Western minnow, Western pygmy perch, Western mud
minnow and Nightfish are dependent on predictable timing and
magnitude of seasonal water flows to trigger migration and for their
survival and breeding success.108 The life cycles of many aquatic
invertebrates, including Carter's freshwater mussel which requires
permanent freshwater to survive, are affected by changes in flow.109
Gilgies rely on moist soils to remain hydrated in the dry season, and
must have access to permanent flows, pools or shallow groundwater for
their populations to be maintained.110
69 The applicant contends that the current hydrological regime in
Quininup Brook below the Lot 14 Dam is not detrimental to any
aquatic fauna species111 and no threatened species had been reported in
the area.112 The applicant says that there was no evidence before the
Tribunal of any species decline in Quininup Brook or that the Lot 14
Dam affected the survival of specific species, such as the Western Mud
Minnow.113 To the contrary, the applicant pointed to evidence from
Mr Green that the dissolved oxygen concentration in Quininup Brook
upstream of Quininup Falls, during one of the hottest days in the
summer of 2024, was within the tolerance range for all native aquatic
fauna species likely to be present in the stream.114
70 The applicant further contends that Mr Green's evidence regarding
transitional flows does not apply to the Lot 14 Dam because it is
leaky,115 and that in respect of the significant contribution the dam
makes for the benefit of the downstream environment, the evidence of
Mr Mulcahy should be preferred.116 It is the applicant's position that
the discharge of water from the Lot 14 Dam through seepage delivers
the very recessional flows that trigger the downstream migration of
105 Mr Green's statement, paras 132 and 153.
106 Mr Green's statement, paras 124 and 126.
107 Mr Green's statement, para 136.
108 Mr Green's statement, paras 124 - 133.
109 Mr Green's statement, paras 135 - 137.
110 Mr Green's statement, paras 140 - 141.
111 Applicant's closing submissions, para E10.
112 Applicant's closing submissions, para E18; Exhibit 17.
113 Applicant's closing submissions, paras E5, E8.
114 Applicant's closing submissions, para E9.
115 Applicant's closing submissions, para E7; ts 44, 9 December 2025.
116 Applicant's closing submissions, para B11.
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aquatic fauna species because the discharge gradually reduces over time
as the water level in the dam drops.117
Findings
71 There was no dispute that the wall of the Lot 14 Dam is 'leaky' in
that it allows some water to seep through (or under) it. However, for
the reasons already given, we are not satisfied that the evidence about
the rate at which water is seeping through the dam wall, particularly
during early and late season transitional flows, is reliable. Further, the
applicant did not produce any independent evidence from a qualified
ecologist to support a finding that the life cycles of aquatic fauna
species downstream of the Lot 14 Dam are unaffected by the dam
because it is leaky.
72 Based on the uncontested evidence of Mr Green, which we accept,
we find that 'shoulder period' or transitional flows play an important
role for the riverine ecology of Quininup Brook, including seasonal
cues for the breeding and migration of aquatic species. We further find,
based on Mr Green's uncontested evidence, that on-stream dams modify
the downstream flow regime and can have a significant impact on
'shoulder period' or transitional flows and dry season low flows.
73 In determining the terms, conditions and restrictions to be included
in a s 5C licence, we must have regard to all matters we consider
relevant, including the matters listed in cl 7(2) of Sch 1 to the
RIWI Act.118 Those matters include whether the proposed taking and
use of water is ecologically sustainable and environmentally
acceptable.119 It also includes whether the proposed taking and use of
water is in the public interest.120
74 The expression 'public interest' is defined in cl 1 of Sch 1 to the
RIWI Act to mean 'public interest having regard to any economic,
social or recreational benefits to the public, or to a section of the
public'. The meaning of the expression 'public interest' is broad in
scope and 'imports a discretionary value judgment to be made by
reference to undefined factual matters confined only by the subject
matter, scope and purpose of the statute in question'.121 The objects of
Pt III of the RIWI Act, which are relevant to delineating the scope of
117 Applicant's closing submissions, para E13; ts 44, 9 December 2025.
118 RIWI Act, Sch 1, cl 15(2).
119 RIWI Act, Sch 1, cl 7(2)(b) and (c).
120 RIWI Act, Sch 1, cl 7(2)(b) and (a).
121 ICM Agriculture Pty Ltd v The Commonwealth [2009] HCA 51; (2009) 240 CLR 140 at [20].
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the 'public interest' are set out in cl 4(1) of the RIWI Act. The objects
which inform the scope of the expression 'public interest' are to provide
for the 'sustainable use and development [of water resources] to meet
the needs of current and future users', 'to promote the orderly, equitable
and efficient use of water resources', and to provide for 'the protection
of [water-dependant] ecosystems and the environment in which water
resources are situated, including by the regulation of activities
detrimental to them'.
75 We find, based on the uncontested evidence of Mr Green, which
we accept, that the WTP Condition and Bypass Condition are
ecologically sustainable and environmentally acceptable because they
aim to protect transitional flows which support the ecological values of
Quininup Brook. We further find that protecting transitional flows is
particularly important to aquatic fauna because of the impact of a
drying climate on streamflow in the South West. Because transitional
flows help protect the downstream ecological values of Quininup Brook
and, ultimately, support the social, recreational and cultural values of
Quininup Falls, we find that the WTP Condition and the
Bypass Condition are in the public interest.
76 Because the Lot 14 Dam reservoir is extensive and supports low
established vegetation, the applicant contends that it is a 'wetland' for
the purposes of the Environmental Protection Act 1986 (WA) (EP Act)
and, consequently, its environmental values must be protected.122
In support of its contention, the applicant relied on the evidence of
Mr Mulcahy. Mr Mulcahy considered that the swamp paperbark
(Melaleuca rhaphiophylla) in the vicinity of the Lot 14 Dam had
adapted to the presence of the dam and 'are in very good health'.123
In Mr Mulcahy's opinion, dams create environmental habitat by
retaining water during dry months which benefit both flora and fauna,
and act as refuges for aquatic invertebrate species during summer
months.124 In contrast, it is Mr Green's opinion that the Lot 14 Dam
does not provide an ecological benefit to the Quininup Brook
catchment.125 He said that farm dams create a closed environment for
aquatic species by restricting where they can access a river system.126
122 Applicant's closing submissions, para 6, A1 and A2; para 12.3; ts 347, 19 March 2026. The applicant also
referred to the Environmental Protection Authority, Environmental Factor Guideline: Inland Waters, 2018 in
support of its contention.
123 Mr Mulcahy's expert report, page 8.
124 Mr Mulcahy's expert report, page 8; Joint Statement, page 8.
125 Joint Statement, page 8.
126 Joint Statement, page 9.
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Mr Green provided the following evidence about the impact of the
Lot 14 Dam on the existing swamp paperbarks:127
…Flooding of Melaleuca rhaphiophylla for prolonged periods can lead
to death of the species as has been observed over recent years in
Lake Joondalup due to high water levels. I observed dead Melaleuca
rhaphiophylla in the [Lot 14 Dam's] footprint on 30/05/2025. …
Areas of Melaleuca rhaphiophylla in good health near the Quininup
Brook tributaries are present due to access to shallow groundwater,
expected to be less than 2 metres below the land surface for large parts
of the year. …
77 In the context of conserving native vegetation, the term 'wetland' is
defined in the EP Act to mean 'an area of seasonally, intermittently or
permanently waterlogged or inundated land, whether natural or
otherwise, and includes a lake swamp, marsh, spring, dampland, tidal
flat or estuary'.128 Whilst we acknowledge the presence of
groundwater-dependent vegetation adjacent to the reservoir of the Lot
14 Dam, including an extensive stand of swamp paperbark,
the evidence produced by the applicant did not support a finding that
compliance with the WTP Condition and Bypass Condition would fail
to maintain the dam's hydrological processes so as to adversely impact
its environmental values. Consequently, for the purposes of cl 7(2) of
Sch 1 to the RIWI Act, we are not satisfied that the ecological
sustainability and environmental acceptability of the conditions, which
are intended to help protect the EWR of the downstream ecosystem, is
diminished by their purported detriment to the riparian flora and fauna
at and around the Lot 14 Dam.
78 We will next consider whether the correct and preferable decision
is to impose the WTP Condition and Bypass Condition on the Current
Licence and, if so, what is the appropriate length of the WTP. Before
doing so, we will consider the policy basis for the imposition of a
winter take period on the Current Licence.
What is the policy basis for a winter take period?
79 The imposition of a winter take period condition, and bypassing
flows outside that period, helps ensure that farm dams do not capture all
transitional flows, particularly in low flow years where the impact of
127 Joint Statement, page 9.
128 EP Act, Sch 5, cl 2. A 'wetland' is similarly defined in s 2 of the RIWI Act to mean a natural collection of
water, whether permanent or temporary, on the surface of any land and includes - (a) any lake, lagoon,
swamp or marsh; and (b) a natural collection of water that has been artificially altered, but does not include a
watercourse.
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dams on downstream ecological values would be greater.129
The seasonal impact of farm dams is shown in Figure 5-3 of the
Sinclair Knight Mertz report entitled, Impacts of Farm Dams on
Streamflow, November 2008.130 Figure 5-3 is reproduced below.
80 As stated earlier, the Whicher Allocation Plan sets out how the
Department will allocate and licence surface water in the Quininup
subarea of the Whicher Area, which includes the Quininup Brook
catchment. The Whicher Allocation Plan provides that on-stream dams
may be subject to licence conditions for when and how streamflow may
be taken.131 It also provides that existing onstream dams may be
required to have a low-flow bypass system132 and that licence
conditions may state when flows must be bypassed during the year.133
81 In determining the terms, conditions and restrictions to be included
in a s 5C licence, we must have regard to the matters listed in cl 7(2) of
129 See Prestidge and Department of Water and Environmental Regulation [2023] WASAT 9 (Prestidge) at
[65]. The winter take period is derived from the sustainable diversion limit (SDL) method. An SDL is an
estimate of the winterfill diversion potential, being an upper limit beyond which there is an unacceptable risk
that additional extractions may degrade the riverine environment: See Estimation of Sustainable Diversion
Limits for South West Western Australian Catchments, Sinclair Knight Mertz, 5 January 2009, page 1;
Respondent's Bundle, page 342.
130 See Respondent's Bundle, page 221.
131 Whicher Allocation Plan, page 10; Respondent's Bundle, page 66.
132 Whicher Allocation Plan, page 10; page 47; Respondent's Bundle, pages 66 and 103.
133 Whicher Allocation Plan, page 46; Respondent's Bundle, page 102.
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Sch 1 to the RIWI Act which include whether the term, condition or
restriction is in keeping with previous decisions of the Minister.134
82 It is the respondent's position that, consistent with the Whicher
Allocation Plan, the WTP Condition and Bypass Condition are
generally imposed on surface water licences within the Quininup
subarea.135 The respondent says that it has been including winter take
period and bypass conditions at licence renewal, and on new licences,
since January 2016.136 At the time that the Current Licence was issued,
the directive to licensing officers was to impose winter take period and
bypass conditions on surface water licences in the Whicher Area.137
83 The applicant says that the Department's approach to the
imposition of the WTP Condition and Bypass Condition, as revealed by
the evidence of Mr Bennett,138 was policy driven despite the
circumstances of the particular case.139 Specifically, the applicant
points to the continuous contribution the Lot 14 Dam makes to
Quininup Brook from seepage throughout the year, including a
significant part of the summer months when there is no prospect of
such a contribution via a by-pass system (in the absence of an
extraordinary rainfall event).140 In addition, at the time the conditions
were imposed, the applicant says that there was no evidence of
environmental detriment to Quininup Brook below the Lot 14 Dam
(which it contends is supported by Mr Green's evidence).141
Findings
84 We find that the imposition of the WTP Condition and
Bypass Condition reflects the purpose of the Whicher Allocation Plan
which is to facilitate the active management of surface water resources
in order to provide greater security for water users and the downstream
environment.142 Further, based on the evidence of Mr Bennett, which
we accept, we find that the Department has consistently imposed winter
take period and by-pass conditions at licence renewal, and on new
licences, since January 2016. We accept Mr Bennet's evidence, and we
134 RIWI Act, Sch 1, cl 7(2)(g)(iv).
135 Respondent's closing submissions, para 28(e); Respondent's Supplementary Bundle filed on
31 October 2025 (Exhibit 2), page 37; ts 190 - 191, 10 December 2025.
136 Respondent's opening submissions, para 55; Respondent's Bundle, pages 733 - 734.
137 Mr Bennett's statement, paras 76, 116 and 139; Respondent's Bundle, pages 733 - 734.
138 ts 200 - 201, 10 December 2025.
139 Applicant's closing submissions, para B16; ts 358, 19 March 2026.
140 Applicant's closing submissions, para B16(i).
141 Applicant's closing submissions, para B16(i).
142 Respondent's Bundle, page 59.
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find, that the respondent imposed the WTP Condition and Bypass
Condition on the Current Licence to help ensure transitional flows in
the tributaries of Quininup Brook are not captured by the Lot 14 Dam
but are permitted to flow downstream to the main channel of Quininup
Brook and, ultimately, to Quininup Falls.143
85 We will next consider whether there is a cogent reason to depart
from the policy that informed the respondent's decision to impose the
WTP Condition and Bypass Condition having regard to, amongst other
things, the unique hydrological features of the Lot 14 Dam.
Is there a cogent reason to depart from the Whicher Allocation Plan?
86 The Whicher Allocation Plan sets out a number of objectives for
managing surface water, which include to protect key ecological,
cultural and social values so they are kept at an acceptable level of risk
from the effect of surface water use.144 It is a policy which is relevant
to our determination because it applies to the management of surface
water in the Quininup subarea and informed the respondent's decision
to impose the WTP Condition and Bypass Condition. We are entitled
to depart from the application of that policy if there are cogent reasons
or a sound basis to do so having regard to the merits of the case.145
Whilst we have considered the provisions of the Whicher Allocation
Plan in making our decision, they cannot be inflexibly applied so as to
fetter the exercise of our discretion.146
87 For the reasons that follow, we do not consider there is a cogent
reason to depart from the application of the policy that informed the
respondent's decision to impose the conditions.
88 First, we are satisfied that the WTP Condition and the Bypass
Condition help ensure that transitional flows in the tributaries of
Quininup Brook are able to flow downstream to meet the EWR of the
main channel of Quininup Brook, including seasonal cues for
the breeding and migration of aquatic species. The Department has not
conducted a site-specific environment or EWR study to determine if the
conditions are required to protect the ecological values of the Whicher
143 Mr Bennett's statement, paras 98 - 107.
144 Respondent's Bundle, page 89.
145 Re Drake and Minister for Immigration and Ethnic Affairs (No. 2) (1979) 2 ALD 634 at 644-5. For a
summary of the principles relating to the application of policy, see More and Water and Rivers Commission
[2006] WASAT 112 at [33] - [36]. See also Prestidge at [110] - [112].
146 Tah Land Pty Ltd v Western Australian Planning Commission [2009] WASC 196 at [37] citing
Clive Elliott Jennings & Co Pty Ltd v Western Australian Planning Commission [2002] WASCA 276;
(2002) 122 LGERA 433 at [24] - [26].
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Area, including Quininup Brook. Nevertheless, for the reasons already
given, we are satisfied that the EWR studies completed in the nearby
Wilyabrup Brook and Cowaramup Brook catchments can be relied on
to provide an understanding of flow rate and ecological function for
Quininup Brook.
89 Second, whilst there was no dispute that the Lot 14 Dam is leaky
and might satisfy the Bypass Condition on certain days in October,147
the rate and period of seepage through the dam wall was not supported
by reliable evidence for the reasons already given. Consequently, we
are not satisfied that the 'leaky' nature of the dam wall would
consistently allow sufficient seepage to reach the downstream
environment and meet the EWR of Quininup Brook, particularly during
dry season low flows. Further, we do not consider that the imposition
of the Bypass Condition will impact the riparian vegetation of the
Lot 14 Dam or that protecting its ecological values outweighs the
importance of safeguarding transitional flows for the benefit of
downstream water-dependent ecosystems.
90 Third, the Lot 14 Dam has a surveyed volume of
112.48 megalitres.148 There was no evidence before us to suggest that
the imposition of the WTP Condition and Bypass Condition would
prevent the applicant from utilising its full AWE of 17 megalitres.
91 Fourth, the Bypass Condition could be achieved by the installation
of a siphon pipe system which is not cost prohibitive.149
Whilst Mr Fogarty considers a siphon would be more effective if it
were installed on the Riparian Dam,150 we are satisfied that older dams,
like the Lot 14 Dam, are suitable for such a system and it would be the
most practical solution.151 Notably, a consultant engaged by
Mr Fogarty to carry out a safety inspection of the Lot 14 Dam
recommended, amongst other things, that a 'simple siphon pipe system'
could be installed to provide a low-flow bypass.152 Further, even with
the siphon in place, the applicant can continue to use surface water for
its established activities on Lot 131 by pumping water from the Lot 14
Dam.
147 The Bypass Condition was likely being met at the time of Mr Owen's site visits on 29 October 2024 and
16 October 2025, see Mr Bennett's statement, paras 171 - 177; ts 198, 200, 211, 10 December 2025.
148 Joint Statement, page 3.
149 Mr Bennett's witness statement, para 147; Mr Mulcahy's expert report, page 6; Respondent's Bundle;
pages 737, 769 and 810; ts 212, 10 December 2025 (Mr Bennett's evidence); ts 248 - 249 (Mr Mulcahy's
evidence).
150 ts 323, 11 December 2025.
151 ts 212, 10 December 2025; ts 249, 11 December 2025.
152 Exhibit 11, page 5.
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92 Fifth, the Lot 14 Dam is the last farm dam before Quininup Falls,
which is a recreational, tourist and culturally significant site in the
South West. As stated above, the scope of the 'public interest' for
the purposes of Pt III of the RIWI Act may extend to economic, social
or recreational benefits to the public, or a section of the public.153
We consider that protecting transitional flows in Quininup Brook,
downstream of the Lot 14 Dam, particularly in a drying climate, is in
the public interest and consistent with the purpose of Part III of the
RIWI Act which is the management of scarce water resources for the
benefit of the public generally.154
93 Because we have not found a cogent reason to depart from the
application of the Whicher Allocation Plan and having regard to
the mandatory relevant considerations in cl 7(2) of the Sch 1 to the
RIWI Act, we are satisfied that the correct and preferable decision is to
impose the WTP Condition and Bypass Condition on the Current
Licence. However, based on the evidence of the joint experts, we
consider that the winter take period should be modified.
What is the appropriate winter take period?
94 Mr Green observed that depending on where the four-month
winter take period is positioned in the calendar year, it is possible that
the dates could capture the entire wet season flow in some years and,
consequently, not pass any transitional flows to the downstream
environment.155
95 The WTP Condition provides that the applicant 'shall only take
water from the watercourse to fill the Lot 14 Dam between 1 June and
30 September, or as otherwise directed by the Department'.
The applicant contends that if the Tribunal decides not to remove the
WTP Condition, the winter take period should be extended to
15 October.156
96 The joint hydrology experts were questioned extensively at the
final hearing about the accuracy of data generated by the streamflow
gauge on Quininup Brook. Dr Jordan used a STEDI157 model to
calculate unimpacted daily flows at the streamflow gauge for 2015 -
153 RIWI Act, Sch 1, cl 1.
154 Crossley at [205].
155 Mr Green's statement, paras 118, 159 - 187.
156 Applicant's SIFC, para 71.
157 Spatial Tool for Estimation of Dam Impacts.
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2019 and 2021.158 He determined the unimpacted flow for the
Quininup Brook catchment using recorded flow, for the days when
reliable data was available (2015 - 2019 and 2021), and daily flows
derived from the Sacramento model for the remaining days between
2000 and 2025.159 For those periods when the Sacramento model was
applied, i.e. before 2015, after 2021 and for the period of missing and
unreliable gauge data in 2020, the Sacramento model under-predicted
the inflow volumes by 4.3% on average.160 For those periods when
gauge data was applied (2015-2019 and 2021) there was no bias in
inflows.161
97 A STEDI model was also used to calculate daily inflows to the
Lot 14 Dam for January 2000 to July 2025. Because the STEDI model
assumed that the daily runoff generated per unit catchment area on each
day between January 2000 and July 2025 was the same across the
catchment upstream of the streamflow gauge and the catchment of
the Lot 14 Dam, Dr Jordan multiplied the unimpacted flows on each
day at the streamflow gauge by 76.3% to produce the daily unimpacted
flow to the Lot 14 Dam.162
98 In Mr Mulcahy's opinion, the clay loam soils above the streamflow
gauge would generate runoff more quickly than the Lot 14 Dam
catchment which comprises around 30% deep sands (which are more
permeable).163 He also considered that the terrain above the streamflow
gauge was of a higher gradient than the catchment of the Lot 14
Dam.164 Based on soil type and terrain, Mr Mulcahy said that the
streamflow gauge would experience greater flows than the flows
upstream of the Lot 14 Dam, which would generate less runoff.165
Consequently, Mr Mulcahy did not agree with Dr Jordan's assumption
that the flow volume into the Lot 14 Dam was 76.3% of the flow
recorded in the streamflow gauge on Quininup Brook.166 Because of
Mr Mulcahy's personal observations and knowledge of soil types, and
the fact that only one tributary was flowing into the Lot 14 Dam on
31 October 2025, the applicant says that Dr Jordan's assumption is
wrong.167 It is the applicant's position that inflow to the Lot 14 Dam is
158 Joint Statement, page 2.
159 Joint Statement, page 3.
160 Dr Jordan's expert report, page 31.
161 Dr Jordan's expert report, page 31.
162 Joint Statement, page 3.
163 ts 86, 9 December 2025; ts 131, 10 December 2025.
164 ts 86, 9 December 2025.
165 ts 118, 122, 10 December 2025.
166 ts 135, 10 December 2025.
167 ts 146 - 47; ts 245; Applicant's closing submissions, C27-28.
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significantly less than 50% of the flow rate measured at the streamflow
gauge.168
99 Dr Jordan said that he had not visited the catchment above the
streamflow gauge.169 He also acknowledged that it might not perform
in the same way as the Lot 14 Dam catchment area because Quininup
Brook, on which the stream flow gauge is located, runs through a
steeper incised channel than the terrain above the dam.170 Nevertheless,
the joint experts agreed, and we find, that the data produced by the
streamflow gauge is the best available data for modelling the likely
runoff from the three tributaries which flow into the Lot 14 Dam.171
100 Mr Mulcahy did not perform any modelling of inflows to the
Lot 14 Dam. In the absence of any other model, we find that
the assessment carried out by Dr Jordan of monthly inflow volumes to
the Lot 14 Dam between January 2000 and July 2025 is based on the
best available stream flow data for the Quininup Brook catchment.
That assessment shows, and we find, that since the year 2000 there
have been inflows in June in 15 - 20% of years, in July in 81 - 100% of
years, in August in 100% of years, in September and October in 96 -
100% of years and in November in 60 - 72% of years.172 We further
find that in every year from 2015 to 2024, there were inflows to the
Lot 14 Dam from the three tributaries in September and October.173
Whilst the STEDI modelling relied on the best available data, we
acknowledge that it might not reflect the precise inflows to the Lot 14
Dam by percentage. For example, Dr Jordan said that he did not adjust
the parameters of the STEDI model to account for potential differences
in soil characteristics174 or the terrain (due to his concerns about how
accurately the contour maps disclose the form of stream channels).175
101 Ultimately, the results of the STEDI modelling support a
modification to the end date of the winter take period because it shows
higher catchment rainfall in September and October. The modelling
also shows that rainfall in June is significantly lower than in July.
Whilst we have found that the data collected by the applicant is not
entirely reliable, we are satisfied that it does show that there were
168 Applicant's closing submissions, C28.
169 ts 83, 9 December 2025.
170 ts 83, 9 December 2025; ts 121, 134, 10 December 2025.
171 ts 119, 122, 10 December 2025.
172 Dr Jordan's expert report, page 34; Table 7-4.
173 Dr Jordan's expert report, page 35; Table 7-5.
174 ts 134, 10 December 2025.
175 ts 83 - 84, 9 December 2025.
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inflows from the eastern tributary of Lot 14 to the Lot 14 Dam between
25 October 2025 and 30 October 2025.176 In Mr Fogarty's experience,
inflows to the Lot 14 Dam do not normally occur in October but
July 2025 had 'extraordinary rainfall'.177
102 For these reasons, and to reduce the risk of transitional flows being
captured by the Lot 14 Dam, we are satisfied that the winter take period
should start on 15 June (rather than 1 June) and end on 15 October
(instead of 30 September). Consequently, we will make an order to
vary the WTP Condition to reflect the change to the winter take period.
We will make a further order to vary the dates set out in the Bypass
Condition to '16 October and 14 June next' to account for the
adjustment in the winter take period. This means that all flows in the
watercourse (of which the Lot 14 Dam forms part) must be bypassed
during that period.
The terms of the WTP Condition
103 The respondent's counsel referred the Tribunal to the decision in
Crossley v English [2025] WASCA 141 (Crossley) in which the WA
Court of Appeal considered whether a downstream landowner has a
private cause of action against an upstream landowner for a breach of
statutory duty under s 20(1)(c) of the RIWI Act.178 Section 20(1)(c) of
the RIWI Act provides that an owner or occupier of riparian land has
the right to take water from a watercourse which runs through their land
to the extent that the flow of water is not sensibly diminished.
104 The trial judge found the respondent had 'sensibly diminished' the
flow of water to the appellant's downstream property.179 Consequently,
the trial judge concluded that the appellant had a cause of action for
breach of statutory duty pursuant to s 20(1) of the RIWI Act but that it
was statute barred because the proceeding was commenced more than
six years after the dam was constructed.180 On appeal, the Court did not
unanimously agree that s 20(1) of the RIWI Act gives rise to a private
cause of action for breach of statutory duty.181 However, the Court
176 Mr Mulcahy's expert report, page 5. A site inspection on 31 October 2025 confirmed that flow entering
the Lot 14 Dam from the central tributary had stopped flowing due to the presence of sand substrate:
Joint Statement, page 5.
177 Mr Fogarty's statement, para 30.
178 Because the properties of the landowners were located in unproclaimed areas, they were subject to the
provisions of Div 2 of the RIWI Act: Crossley at [24].
179 Crossley v English [No.2] [2024] WASC 268 (Crossley v English [No. 2]) at [332].
180 Crossley v English [No.2] at [397] - [401].
181 Crossley at [107] per Thomson J; [208] per Mitchell & Archer JJA.
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unanimously agreed that such an action would be statute barred and
dismissed the appeal for that reason.182
105 The Court in Crossley explained that a dam constructed on a
watercourse 'takes' water for the purposes of the definition of 'take' in
s 2(1) of the RIWI Act because the dam is 'stopping, impeding or
diverting the flow of water'.183 As a result, an action for breach of
s 20(1) of the RIWI Act must be commenced within the six year
limitation period from the dam's construction.184 Thomson P
considered the meaning of 'stopping, impeding or diverting the flow of
water' in s 2(1) of the RIWI Act and determined that it is 'concerned
with a singular event which affects the flow of water, rather than an
event that continually affects the water which is flowing'.185
His Honour's interpretation of 'stopping, impeding or diverting the flow
of water' was supported because, by reason of the definition of
'watercourse' in s 3 of the RIWI Act, once a dam is constructed on a
watercourse it becomes part of the watercourse.186 Consequently, in the
context of s 20(1)(c) of the RIWI Act, Thomson P said that it was
difficult to see that a dam, which becomes part of the watercourse,
could be regarded as continually taking water from the watercourse.187
106 Because the installation of the Lot 14 Dam was the event that
'takes' water for the purposes of s 2(1) of the RIWI Act, the
respondent's counsel suggests that the WTP Condition could be
modified to delete the word 'take' and substitute it for the word 'allow'
so that the applicant must only 'allow' water from the watercourse to fill
the dam between 1 June and 30 September (or another date range as
determined by the Tribunal).188
107 In our view, the respondent's proposed amendment is unnecessary
because the use of the word 'take' in the WTP Condition is consistent
with the language of s 5C of the RIWI Act, which provides, relevantly,
that a person must not 'take' water from any watercourse except under a
licence granted by the Minister in accordance with Sch 1 to the
RIWI Act.
182 Crossley at [152] - [153] per Thomson P; [209] per Mitchelle & Archer JJA.
183 Crossley at [123]; see para (b) of the definition of 'take' in RIWI Act, s 2(1).
184 Crossley at [151].
185 Crossley at [122].
186 Crossley at [123].
187 Crossley at [125].
188 Respondent's closing submissions, para 11.
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108 Further, for the purposes of a s 5C licence, we are satisfied that the
Lot 14 Dam is continually taking water from Quininup Brook.
According to Crossley, the Lot 14 Dam would have 'taken' water when
it was installed by the singular event of affecting the flow of water and,
therefore, must cease to 'take' water if the dam is removed from
Quininup Brook. Because the 'take' ceases immediately upon the dam's
removal, we consider that the dam is 'taking' (that is, it stops, impedes
or diverts the flow of) water from the watercourse continually up until
that point in time.
109 For these reasons, we consider that the use of the word 'take' in the
WTP Condition is appropriate.
110 As a consequence of Crossley, the applicant contends that it is not
required to hold a s 5C licence to lawfully 'capture' surface water
because the Lot 14 Dam forms part of the watercourse and the 'take'
occurred by the installation of the dam.189 (The applicant, however,
acknowledged it would require a licence to pump water from the Lot 14
Dam).190 Consequently, the applicant contends that the WTP Condition
and Bypass Condition are ultra vires by purporting to prohibit the
applicant from 'capturing' water in the Lot 14 Dam outside particular
months of the year.191 We reject those contentions because the
applicant is taking water from a watercourse (of which the Lot 14 Dam
forms part) by stopping, impeding or diverting the flow of water by
virtue of the presence of the dam wall, and the watercourse is located in
a proclaimed area to which s 5C of the RIWI Act applies. Finally, for
the reasons already given, we do not consider that Crossley affects the
Department's policy to impose a winter take period on new surface
water licences, and at licence renewal, or gives rise to a cogent reason
to depart from the application of that policy to the Lot 14 Dam as the
applicant contends.192
111 As stated above, the modelling of flow rates for the Quininup
Brook catchment does support an amendment to the WTP Condition to
account for higher September and October rainfall. Also, because the
applicant pumps water from the Lot 14 Dam to the Lot 131 Dam, we
will amend the WTP Condition to refer to the dam on Lot 14 to avoid
189 Applicant's closing submissions, para 4.7; ts 350, 19 March 2026.
190 Applicant's closing submissions, para 4.5; ts 350, 19 March 2026.
191 Applicant's closing submissions, paras 4.6, and 4.11; ts 249, 19 March 2026.
192 ts 355, 19 March 2026.
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ambiguity.193 Consequently, we will vary the respondent's decision so
that the terms of the WTP Condition are as follows:
3. The licensee shall only take water from the watercourse to fill
the dam on Lot 14 between 15 June and 15 October or as
otherwise directed by the Department of Water and
Environmental Regulation.
Conclusion
112 The WTP condition and Bypass Condition are not exclusive to the
Current Licence; the Department has consistently applied a winter take
period on new surface water licences in the Whicher Area or at licence
renewal.
113 In determining whether the Current Licence should be granted
subject to the WTP Condition and the Bypass Condition, we must seek
to ensure the objects set out in s 4(1) of Pt III the RIWI Act are
achieved.194 We are also required to consider the matters set out in
cl 7(2) of Sch 1 to the RIWI Act. Otherwise, we can have regard to all
matters that we consider relevant, which includes the provisions of the
Whicher Allocation Plan, the policy basis for the imposition of a winter
take period on the Current Licence.
114 The winter take period helps protect the ecological values of
Quininup Brook, including the habitat of downstream aquatic fauna, by
the maintenance of transitional flows, which is consistent with the
objects of the RIWI Act to protect water-dependent ecosystems.
Maintaining transitional flows is not only ecologically sustainable but
also in the public interest because those flows help support the
environmental, social and cultural values of the Quininup Brook
catchment, including Quininup Falls.
115 The Lot 14 Dam has unique hydrologic features in that it allows
the flow of water downstream via a 'leaky' dam wall. However, we
have not identified a cogent reason to depart from the application of the
Whicher Allocation Plan having regard to the circumstances of this
case. Based on the evidence, we are not satisfied that seepage from the
dam wall is sufficient to consistently meet the EWR of Quininup
Brook, particularly in respect of transitional flows, and dry season low
flows. Nevertheless, the modelling of flow rates for the Quininup
Brook catchment does support an amendment to the winter take period.
193 Mr Fogarty's statement, para 26.
194 RIWI Act, Sch 1, cl 4(3).
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116 Consequently, we conclude that the correct and preferable
decision is to allow the review application in part and vary the
respondent's decision so that the WTP Condition and the Bypass
Condition read as follows:
3. The licensee shall only take water from the watercourse to fill
the dam on Lot 14 between 15 June and 15 October or as
otherwise directed by the Department of Water and
Environmental Regulation.
4 The licensee shall bypass all flows in the watercourse between
16 October and 14 June next.
Orders
The Tribunal orders:
1. The application for review is allowed in part.
2. The respondent's decision made on 13 September 2023 to grant
the applicant a licence to take surface water pursuant to s 5C of
the Rights in Water and Irrigation Act 1914 (WA) by
Instrument No. SWL209115(1) is varied as follows:
(a) The licensee shall only take water from the watercourse
to fill the dam on Lot 14 between 15 June and
15 October or as otherwise directed by the Department
of Water and Environmental Regulation.
(b) The licensee shall bypass all flows in the watercourse
between 16 October and 14 June next.
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ANNEXURE A
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I certify that the preceding paragraph(s) comprise the reasons for decision of the
State Administrative Tribunal.
MS C BARTON, MEMBER
2 JULY 2026
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