A NSW Government website

Genetic typing of M. sydneyi across estuaries of different QX risk-groups


Surveillance undertaken through previous years (2002-2005) has indicated that M. sydneyi is present in the majority of NSW estuaries, although outbreaks of QX disease only occur in some. In order to understand whether variation in the M. sydneyi strain could account for these differences in disease expression, key M. sydneyi genes from archived oyster samples collected from medium and high risk estuaries were sequenced and compared (Table 1).

Table 1. Origin and year of collection of QX-infected Sydney rock oyster samples used in this study.

Sample ID

Year collected

Estuary of origin

Estuary QX risk rating

M16-04749-6

2016

Hawkesbury River

High

M16-06827-85

2016

Georges River

High

M20-05667-13

2020

Macleay River

High, but infrequent outbreaks

M20-06326-17

2020

Richmond River

High

M20-06983-41

2020

Brunswick River

Medium

M21-11844-24

2021

Richmond River

High

M22-17260-24

2022

Stradbroke Island, Qld

N/A

M22-17262-10

2022

Stradbroke Island, Qld

N/A

M22-17475-7

2022

Stradbroke Island, Qld

N/A

M23-06441-24

2023

Port Stephens

High

Preliminary analysis of the sequence data suggests very little sequence diversity amongst M. sydneyi strains in high and medium QX risk estuaries. While some variant nucleotides were observed in the ITS2 region of the sequences, these are likely attributable to allelic variation. Only one strain, M22-17475-7 from Queensland showed a sequence difference (25 bp deletion) in the ITS 2 region; however, this was absent from the 2 other Queensland strains examined.

In addition, SROs from low-risk estuaries, where QX disease does not occur, were collected and screened for the presence of M. sydneyi to obtain material for genetic comparison.

  • April 2023 - Wallis Lake (n = 150) and Wagonga Inlet (n = 150)
  • March 2024 - Wallis Lake (n = 250), Wagonga Inlet (n = 250) and Tuross Lake (n = 250) [Figure 1]
  • March and April 2025 - Wallis Lake (n = 250), Wagonga Inlet (n = 250) and Tuross Lake (n = 250)

Despite prior molecular detection of M. sydneyi in these estuaries at between 7 and 25% prevalence, no PCR positives were detected from the 1,800 oysters collected.

Map of QX Surveillance sampling zones