4.1 Climatological characteristics of Australian bushfire conditions
The mean-state and the 90th percentile extreme FFDI values, calculated at each grid point across Australia for the entire study period 1876–2014 under consideration, are shown in Fig. 2.
Overall, this shows that the austral spring and summer seasons are when dangerous fire weather conditions generally occur throughout most of Australia, though the Northern Territory and parts of Western Australia and Queensland can also experience high FFDI values during the austral autumn and winter seasons. The coastal regions around the eastern parts of Australia are slightly more vulnerable to bushfire threats during austral spring than in summer, consistent with previous studies (Luke and McArthur 1978; Dowdy 2020).
However, it is important to note that year-to-year variability in the mean-state and extreme FFDI days across Australia can be considerably large. These spatio-temporal variations can be attributed to the variability in various climatic drivers that influence the Australian climate. In the next sections, we will look at the effects of various natural climate drivers that modulate FFDI conditions over Australia for different seasons.
4.2 Effects of natural climate variability
We examine the effects of various climate drivers, namely ENSO, IOD, SAM and IPO, on both the mean FFDI conditions as well as on the extreme conditions for all seasons across Australia. As dangerous fire weather conditions in Australia often occur during the austral spring and summer seasons, we primarily focus on these two seasons in this study. Also, to better understand how the relationship between climate drivers and FFDI has potentially evolved over time, we divided the study period into two epochs: the first epoch comprises the period from 1876–1945 and the second epoch, 1945–2014. This particular approach is intended to help enable statistical analysis of differences between the climatological averages of the first and second halves without making assumptions about physical changes in climate at a particular point.
4.2.1 ENSO-FFDI
ENSO plays a dominant role in modulating the extreme FFDI days (Figs. 3 and 4) and monthly mean FFDI conditions (Supplementary Figs. 1 and 2) in both spring and summer seasons, as well as in other seasons (Supplementary Figs. 3–6). In other words, a positive phase of ENSO increases the likelihood of dangerous fire weather conditions. However, when we examined the ENSO-FFDI relationship for the two separate epochs (i.e., 1876–1945 and 1945–2014), we found a considerable strengthening of the relationship in the second epoch for all seasons compared with the first epoch in many regions, such as shown in Figs. 3 and 4 for the spring and summer seasons, respectively.
During the austral spring season of the first epoch, a statistically significant positive correlation pattern could be observed over southeastern Australia (Fig. 3a). However, as we move into the second epoch, we see a statistically significant positive correlation over a much larger region of Australia (Fig. 3b). For the austral summer (DJF), a negative correlation with ENSO for parts of western Australia is the main feature apparent in the first epoch, while a positive correlation is apparent over eastern Australia and northern tropics during the second epoch (Fig. 4b). However, we note that the strength of the ENSO-FFDI relationship is relatively weak during the DJF season (Figs. 4a, b) compared with the SON season (Figs. 3a, b).
For the ENSO-FFDI relationship during the austral autumn, regions with a significant positive correlation are only around northeastern Australia (Supplementary Fig. 3b). Here we can again observe a similar strengthening of the ENSO-FFDI relationship during the second epoch compared to the first epoch. For the winter season (Supplementary Figs. 4a-4b), there is a substantial increase in the areas with a significant positive correlation in the southeastern parts of Australia during the second epoch compared with the first epoch. Though these areas have a significant positive correlation pattern, the values at these locations in the FFDI climatological maps (Figs. 2c – 2f) are the lowest among the four seasons.
4.2.2 IOD-FFDI
The IOD can influence fire weather conditions across Australia, though the magnitude of variability differs between seasons and regions (Figs. 3 and 4; Supplementary Figs. 1–6).
During the spring season (i.e., SON months), there is a positive correlation pattern between IOD and both mean FFDI and extreme FFDI days over most of Australia, noting that the statistically significant relationship is mainly around the southeastern Australian region (Fig. 3c and Supplementary Fig. 1c). This positive correlation strengthens and expands into south and western Australia in the second epoch (Fig. 3d and Supplementary Fig. 1d). For the DJF season, in the first epoch, there are significant positive FFDI-IOD correlations in parts of northern Australia, but during the second epoch, those regions are no longer indicated as significant, with the main region of significant correlations occurring in eastern Australia, with a negative sign (Figs. 4c, d and Supplementary Figs. 2c, d). This is likely to be associated with IOD having a more robust influence on Australian weather conditions during the austral spring in contrast to summer when the decaying phase of the IOD occurs (Zhao and Hendon, 2009; Hendon et al., 2012; Lim and Hendon, 2017).
During the first epoch of the austral autumn season, we observe a strong positive correlation between IOD and extreme FFDI days (Supplementary Fig. 3c), as well as between IOD and mean FFDI (Supplementary Fig. 5c), over entire Australia except for the western region around the coast. In the second epoch, a general weakening of the FFDI-IOD relationships could be observed (Supplementary Fig. 3d, 5d).
In the winter season, we see a similar positive correlation pattern over southern and western Australia (Supplementary Figs. 4c,4d, 6c, 6d) as we observed in the spring season (Figs. 3c, 3d and Supplementary Figs. 1c, 1d). This is anticipated as IOD is active during the austral winter and spring seasons (Zhao and Hendon, 2009; Hendon et al., 2012; Lim and Hendon, 2017). Note that even though we observe a strong significant positive correlation over the southern half of Australia during the winter, it does not necessarily indicate dangerous bushfire conditions. As we have previously highlighted, the mean extreme FFDI values over the aforementioned regions during the winter months are very low (Figs. 2c-2f), and so the results need to be interpreted in this context accordingly.
4.2.3 SAM-FFDI
SAM is another key climatic driver that affects fire weather conditions, particularly in the southern parts of Australia, where the negative phase of SAM is associated with reduced rainfall during austral spring and summer, and hence enhanced bushfire conditions (Harris and Lucas 2019).
For the spring season in the first epoch, there is a strong negative correlation between SAM and FFDI values (for both extreme and mean-state FFDI values) across most of Australia, noting exceptions around Victoria and Northern Territory (Fig. 3e and Supplementary Fig. 1e). In the second epoch, there is a significant negative correlation over most of the eastern half of Australia (Fig. 3f and Supplementary Fig. 1f). During the austral summer, there is a strong negative correlation in eastern and northern Australia, particularly during the first epoch and to a somewhat lesser degree during the second epoch (e.g., Fig. 4e, 4f).
For autumn (MAM), the SAM-FFDI correlations are negative in parts of eastern Australia during the first epoch (Supplementary Fig. 3e) and over WA in the second epoch (Supplementary Fig. 3f). For winter, there is only a relatively small region in northern Australia with significant positive correlations during the first epoch, while in the second epoch, there is a relatively large region with significant negative correlations across the eastern and central regions of Australia (Supplementary Fig. 4f).
4.2.4 IPO-FFDI
The IPO is examined here in relation to fire weather conditions. It is important to note that measures such as the TPI index used for monitoring IPO can have a considerable association with ENSO indices due to the nature of their derivations, such that we have first removed ENSO influences on the IPO using a linear regression approach based on seasonal values of TPI and Niño-3.4. The residual IPO data, referred to here as TPI*, can then be used to evaluate the relationship between IPO and FFDI that is not associated with the IPO-ENSO relationship. Moreover, due to the low frequency of variability, the TPI itself has very high autocorrelation (r = 0.96 for spring and summer time series used in this study), such that statistical degrees of freedom are adjusted here when evaluating the significance of the statistical relationship between IPO and FFDI as described in Section 3.3 (Panofsky and Brier, 1958).
Figure 5 shows correlations between TPI* and FFDI during the austral spring and summer presented individually for the first and second epochs of the study period. During the first epoch (Fig. 5a, c), we see a moderately high positive correlation pattern in eastern Australia with weaker or negative correlations in some western regions, noting that these correlations are not statistically significant (at the 95% confidence level used in this study). This lack of statistical significance relates to the strong autocorrelation of the IPO, which reduces the degrees of freedom, as discussed earlier. On the contrary, we notice a considerable weakening in the relationship in the correlations during the second epoch for spring and summer. It shows little resemblance to those of the first epoch for each of those seasons, with certain regions now having a weak positive correlation pattern in NSW and WA (Fig. 5b, d). The correlations are once again not statistically significant. Though the primary focus here is on the relationship between FFDI values and IPO during the austral spring and summer, we also included the results for autumn and winter (Supplementary Fig. 7).
4.3 Synergetic relationship between drivers
In this section, we focus on the combined effects of ENSO, IOD and SAM on Australian fire weather conditions. In particular, we look at eight different combinations resulting from two phases each for these three modes of variability (Fig. 6 and Supplementary Figs. 8–10 for the second epoch and Supplementary Figs. 11–14 for the entire period under consideration). Note that there are no exact definitions for different phases of these climate modes, with all approaches being somewhat arbitrary, with a number of approaches considered in this study. For the aims of this analysis, around examining different combinations of multiple modes of variability using a systematic approach, a large sample size is beneficial to help populate the various combinations as well as possible. Given this focus for the analysis here, we have used 'zero' threshold to separate each mode into their respective 'negative' and 'positive' phases. However, even after following this criterion, we find some combinations of climatic modes still have very few samples, and so the following results must be interpreted accordingly, particularly for cases with relatively low sample sizes. We also examined results using a more common approach for defining phases of these climate drivers using higher magnitude threshold values, as shown in Supplementary Fig. 15. Using that more restrictive approach, with fewer cases with data available for the phase combinations, the available results are broadly similar in sign to those shown using the more inclusive approach in Fig. 6.
During the austral spring season, extreme FFDI days in southeast Australia are shown to be more likely during positive IOD conditions, with a somewhat surprising result being that this is largely independent of the ENSO conditions (see Figs. 6). That result is based on 11 seasonal average values in total for positive IOD and SAM conditions (comprising 8 positive ENSO conditions and 3 negative ENSO conditions), such that results should be considered accordingly given that sample size and acknowledging that Australia can have substantial interannual variability in fire weather conditions. ENSO conditions have a larger influence on the FFDI values in central eastern Australia, with more frequent extreme FFDI occurring for positive ENSO conditions (based on the Niño-3.4), which corresponds to conditions more similar to El Niño rather than La Niña. These extreme FFDI conditions become even more likely if the combination of positive IOD and positive ENSO conditions occurs during the negative phase of SAM (Fig. 6e). We also see very high values of extreme bushfire conditions over Australia during a combination of negative ENSO, positive IOD and negative SAM (Fig. 6g), noting that there are only three realisations for this combination. We also notice considerably high extreme FFDI days over Australia during the co-occurrence of positive ENSO, positive IOD and negative SAM phases (Supplementary Fig. 8e) in the summer season. High extreme FFDI days are also noticed over eastern Australia during positive ENSO, negative IOD and negative SAM (Supplementary Fig. 8f). This result is somewhat consistent with the observed positive ENSO – FFDI, negative IOD – FFDI and negative SAM – FFDI correlation patterns during the summer months across eastern Australia (Fig. 4), as discussed in the previous section.
As for the austral autumn season, we again see a considerably high frequency of extreme FFDI days across Australia during positive ENSO, positive IOD and negative SAM combination (Supplementary Fig. 9e), particularly over the western regions. Similarly, the combination of a negative IOD and negative SAM also shows a high frequency of extreme FFDI days during summer across many regions of Australia (Supplementary Fig. 9f and Supplementary Fig. 9h). However, during the winter months, we see the highest frequency of FFDI extreme days during a combination of positive ENSO, positive IOD and positive SAM (Supplementary Fig. 10a) across western and southeastern Australia. This is closely followed by positive ENSO, negative IOD and negative SAM combination in terms of extreme FFDI values during the winter season (Supplementary Fig. 10f).
In conclusion, it can be said that the highest likelihood of dangerous bushfire conditions across Australia is during a combination of positive ENSO, positive IOD and negative SAM modes of variability. The regional features shown here can also be useful for practical fire management applications, including as guidance material for upcoming seasons, given that these modes of variability can sometimes be predictable several months in advance. A key feature of this study is that the long time period of the reanalysis data used here enables a large sample size to help produce small subsets for different combinations of modes of variability, with figures such as Fig. 6 helping to provide new insight on the combined influences of these key modes of variability on Australian fire weather conditions.
4.4 Independent Influence of each driver on the mean FFDI
There are interdependencies between different modes of climate variability, even to the extent that the climate signal of one mode may be contaminated by the other (e.g., as noted for the IPO-ENSO interdependencies detailed in Section 4.4). Therefore, in order to assess the relative roles between mean fire weather conditions and ENSO, IOD and SAM independently, multiple linear regression has been used (Snecdecor and Cochran, 1989; Lim et al., 2021). We first detrended the mean seasonal FFDI time-series and the key climate indices (i.e., Niño-3.4, DMI and AOI) before creating a multiple linear regression model for each grid point to prevent any contamination in the analysis arising from its inherent trend. This detrended data was normalised before creating the regression model so that all the input variables have unit variance (Snecdecor and Cochran, 1989) for easy comparison.
Multiple linear regression model during the spring season shows positive coefficients associated with ENSO (i.e., Nino 3.4 index) across parts of northern and inland-eastern Australia (Fig. 7a), indicating enhanced FFDI values in those regions during El Niño conditions. As for IOD (using DMI), positive coefficients occur across parts of southern Australia, particularly for Victoria in southeast Australia and in southern South Australia, with some regions of negative correlations in parts of central Queensland and eastern NSW (Fig. 7b). Negative correlations occur for SAM in some parts of eastern Australia and through central Australia into southern Western Australia, with positive correlation shown for parts of weather Australia and in the southeast, including Tasmania, as well as a thin strip along the central east coast into Queensland (Fig. 7c).
For summer, a positive coefficient of Nino 3.4 could be seen across many regions of Australia (Fig. 8a). For IOD in summer, the correlations are positive in western Australia and negative in parts of eastern Australia (Fig. 8b). For SAM in summer, the correlations are positive in sign for parts of South Australia and negative in sign across parts of eastern, northern and western Australia (Fig. 8c).
These patterns shown in Figs. 7 and 8 are broadly similar to our correlation patterns for mean seasonal FFDI and the respective climatic drivers (Supplementary Figs. 1–2). Correlation patterns between mean seasonal fire weather conditions and key climatic drivers during austral autumn and winter (Supplementary Figs. 5–6) are also found to be similar with multiple linear regression plots for the respective seasons (Supplementary Figs. 24–25).
Concluding from the multiple linear regression analysis across all four seasons, ENSO is an important climatic driver influencing the fire weather conditions over Australia, with IOD and SAM having significant independent influences too. In particular, our results demonstrate this quantitatively, providing details on how these influences vary spatially through Australia and between different seasons. This new insight is intended to be useful guidance for operational season prediction of fire danger in Australia by providing new insight from this long data set to help understand which climate driver (or drivers) are most important for influencing the fire weather conditions for a given region and season.
4.5 Environmental controls
The seasonal relationship between each of the input climatic variables (daily maximum temperature, wind speed, rainfall and relative humidity) for FFDI and the three key climatic drivers (i.e., ENSO, IOD and SAM) are analysed using a similar correlation technique (Figs. 9–12 and Supplementary Figs. 18–29). This enables us to understand the changing relationship between FFDI and the respective climatic drivers between the two epochs. But first, we validated the correlation patterns in the relationships with previous studies (Risbey et al., 2009; Abram et al., 2021) for similarity and consistency. The second emphasis is on how the relationship between these variables with the climatic driver changes in the second epoch and, consequently, their influence on FFDI.
During the austral spring and summer season, we notice stronger magnitude correlations in the second epoch compared to the first for temperature (Figs. 9a, 9b and Supplementary Figs. 18a, 18b), rainfall (Figs. 11a, 11b and Supplementary Figs. 20a, 20b), and relative humidity (Figs. 12a, 12b and Supplementary Figs. 21a, 21b). This is consistent with the enhancement of the FFDI-ENSO relationships from the first to the second epochs (Figs. 3a, 3b, 4a, 4b and Supplementary Figs. 1a, 1b, 2a, 2b), noting that the stronger magnitude positive correlations for temperature and stronger magnitude negative correlations for relative humidity and rainfall tend to contribute to the enhanced FFDI-ENSO relationships. There is little change indicated between the two epochs for the wind speed-ENSO relationships (Figs. 10a, 10b and Supplementary Figs. 19a, 19b).
During the spring season, a stronger positive correlation is seen for the IOD-temperature relationship from the first to the second epochs (Figs. 9c and 9d) and stronger negative correlations for the IOD relationships with wind speed (Figs. 10c and 10d) and relative humidity (Figs. 12c and 12d).
For SAM, a negative correlation is shown with temperature (Figs. 9e and 9f) over eastern Australia and a positive correlation with rainfall (Figs. 11e and 11f) and relative humidity (Figs. 12e and 12f). We also notice an enhancement of these relationships over Eastern Australia, along with the negative FFDI-SAM (Figs. 3e and 3f) relationship in the second epoch as compared to the first epoch. For wind speed-SAM relationships, the correlations are negative in southeast Australia, with some regions of positive correlations in northeast Australia near the coast (Figs. 10e, 10f), which is not similar to the correlations seen for FFDI-SAM in Figs. 3e and 3f, indicating that the other weather variables have a more dominant influence than wind speed on the FFDI-SAM relationship.
We have then repeated our analysis on autumn (Supplementary Figs. 22–25) and winter (Supplementary Figs. 26–29) as well. We again find temperature (Supplementary Figs. 22 & 26), rainfall (Supplementary Figs. 24 & 28) and relative humidity (Supplementary Figs. 25 & 29) have an influence on the relationship between the climatic drivers and FFDI in many cases (Supplementary Figs. 1–2 & 5–6). Similarly, here also, wind speed does not seem to influence the change between the epochs in fire weather for many locations across Australia (Supplementary Figs. 23 & 27).