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Assessing Drought Vulnerability in the Brazilian Atlantic Forest Using High Frequency Data

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08 January 2024

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11 January 2024

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Abstract
This research investigates the exposure of plant species to extreme drought events in the Brazilian Atlantic Forest, employing an extensive dataset collected from 205 automatic weather stations across the region. Meteorological indicators derived from hourly data, encompassing precipitation, maximum and minimum air temperature, were utilized to quantify past, current, and future drought conditions. The dataset, comprising 10,299,236 data points, spans a substantial temporal window and exhibits a modest percentage of missing data. Missing data were excluded from analysis, aligning with the decision to refrain from imputation methods due to potential bias. Drought quantification involved the computation of the Aridity Index, the analysis of consecutive hours without precipitation, and the classification of wet and dry days per month. Mann-Kendall trend analysis was applied to assess trends in evapotranspiration and maximum air temperature, considering their significance. The hazard assessment, incorporating environmental factors influencing tree growth dynamics, facilitated the ranking of meteorological indicators to identify regions most exposed to drought events. The results revealed consistent occurrences of extreme rainfall events, indicated by positive outliers in monthly precipitation values. However, significant trends were observed, including an increase in daily maximum temperature and consecutive hours without precipitation, coupled with a decrease in daily precipitation across the Brazilian Atlantic Forest. No significant correlation between vulnerability ranks and weather station latitudes and elevation were found, suggesting geographical location and elevation does not strongly influence observed dryness trends.
Keywords: 
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1. Introduction

The Brazilian Atlantic Forest, once sprawling across 150 million hectares and dominating the country’s coastal regions, has undergone significant transformations over the centuries. Originally contiguous, the forest has evolved into fragmented patches, especially along the Brazilian coast, due to historical land use changes and urban expansion [13]. This fragmentation, particularly noticeable in smaller fragments of less than 50 hectares, has placed a substantial portion of the forest’s diverse biodiversity at risk of extinction [14,15,16]. Fragmented landscapes often experience edge effects driven by abiotic factors like water, wind, and temperature, pushing plant communities toward early successional stages [17,18,19,20].
As one of the planet’s most biodiverse ecosystems, the Brazilian Atlantic Forest faces escalating threats, with climate change posing a formidable challenge. The biome’s intricate web of life and ecological significance is now confronted with shifting aridity patterns, exacerbated by habitat fragmentation and ecological succession processes [1]. Recent ecological shifts in the Atlantic Forest have intensified, contributing to increased aridity and prompting concerns about the separation of Amazonian and Atlantic Forest lineages in Brazil [2].
Amidst these ecological transformations, environmental variables, particularly precipitation, play a pivotal role in shaping the vitality of the Atlantic Forest. Anthropogenic pressures and climate change effects loom large, and long-term forecasts signal a concerning decline in precipitation levels [3]. Such changes could significantly impact the delicate balance of this vulnerable ecosystem [4,5]. This study, conducted between 2000 and 2022, seeks to delve into the repercussions of evolving aridity patterns on the Brazilian Atlantic Forest.
This study focuses on meteorological indicators to unveil nuanced trends and pinpoint regions undergoing substantial alterations in aridity conditions. By scrutinizing the impact of changing climate patterns on the Atlantic Forest, this research aims to contribute valuable insights into the ecological dynamics of this biome. Subsequent sections provide a description of the methodology, data, and outcomes, shedding light on the complex relationship between climate variability and the status of the Brazilian Atlantic Forest.

2. Materials and Methods

We adopted the boundaries of the Brazilian Atlantic forest to be congruent with those delineated for the Atlantic forest biome by the Instituto Brasileiro de Geografia e Estatística (IBGE). The definition of the Atlantic forest biome by IBGE was based on an extensive process involving literature review, interinstitutional validation, and field surveys to verify the presence of the physical-biotic environment and historical evidence of the Atlantic forest within the demarcated boundaries [6]. These boundaries were sourced from TerraBrasilis, a platform managed by the Instituto Nacional de Pesquisas Espaciais (INPE), which facilitates data organization, accessibility, and utilization for Brazil’s environmental monitoring efforts.
To assess the exposure of plant species to extreme drought events in the Brazilian Atlantic forest, we relied on meteorological indicators. These indicators were derived from hourly data of precipitation, maximum and minimum air temperature recorded at 205 automatic weather stations, accessible from the Instituto Nacional de Meteorologia (INMET) database [https://bdmep.inmet.gov.br, accessed in August 2023]. An overview of these datasets, including station codes, sample sizes, monitoring periods, and the percentage of missing data, is provided in the supplementary materials. The geographic distribution of the 205 automatic weather stations as well as the boundaries for the Atlantic forest used in this study are presented in Figure 1. This dataset stands as an extensive and robust compilation, with a total of 10,299,236 data points. Spanning a broad temporal window, from distinct station-specific start dates to a standardized endpoint on December 31, 2022, the dataset exhibits a relatively modest percentage of missing data.
Past, current, and future drought conditions were quantified using several meteorological indicators, including the number of consecutive hours without precipitation, the number of dry and wet days per month, the Aridity Index, and the Mann-Kendall test statistic (Z) for trend analysis in evapotranspiration (ET) and maximum air temperature ( T m a x ). The choice of these indicators was motivated by their relevance to recent severe drought events [11]. We opted against employing imputation methods to replace missing data, as this approach can introduce systematic bias into the meteorological indicators [7,8]. Consequently, all missing data were excluded from the analysis, and the accumulated or averaged values resulting from any missing hourly data from the 205 automatic weather stations were disregarded.
The Aridity Index was computed as the ratio of monthly precipitation to evapotranspiration. Monthly precipitation values were determined by aggregating the available hourly precipitation data, while monthly evapotranspiration values were calculated by aggregating daily reference crop evapotranspiration estimates. These daily estimates were generated using the Hargreaves and Samani equation [9], with input data encompassing measured hourly maximum and minimum air temperatures, elevation, and latitude.
The classification of wet and dry days per month was performed using a precipitation threshold of 0 mm per weather station. Days with precisely 0 mm of precipitation were categorized as dry, while those with precipitation exceeding 0 mm were classified as wet. Subsequently, the median values for the number of wet and dry days per month were employed as meteorological indicators to gauge drought exposure.
To determine the duration of consecutive hours without precipitation, we analyzed sequences of hours with no recorded precipitation. In instances of missing data within a sequence, we adopted a conservative approach by considering two distinct sequences. This approach was necessary as missing data could inadvertently elongate the periods to be without precipitation.
Mann-Kendall (MK) trend analysis was employed to examine the daily evapotranspiration estimates and maximum air temperature data at each weather station. A trend was considered statistically significant when the associated p-value was less than 0.05. The MK test statistics, Z and S, were used to assess both the presence and the strength of a monotonic upward or downward trend in daily evapotranspiration and maximum air temperature. The MK test statistic Z was further utilized as an indicator for evaluating potential future drought exposure.
Lastly, we conducted a hazard assessment by ranking the meteorological indicators calculated for each weather station, which allowed us to identify the regions most exposed to drought events. This hazard assessment was developed, taking into consideration environmental factors that influence tree growth dynamics in the Brazilian Atlantic forest under drought conditions [10], as well as the amount of data available after the data filtering process for missing data.

3. Results and Discussion

We used boxplots to visualize the distribution of accumulated monthly precipitation for all 205 automatic weather stations in the Brazilian Atlantic forest. They provide range, median, and distribution of values at each weather station during their monitoring period. The boxplots are presented in Figure 2. Figure 2 reveals the presence of positive outliers across most of the weather stations, which indicates instances of extreme rainfall events. These events are characterized by precipitation values significantly higher than the majority of the data points. The consistent occurrence of positive outliers across various weather stations implies that extreme rainfall events are a recurring phenomenon in the Brazilian Atlantic forest.
The Mann-Kendall (MK) test assessed the presence and strength of monotonic trends in the time series data. We assumed that trends were statistically significant when the p-value was less than 0.05. The results of the MK trend analysis are summarized in Figure 3. A substantial majority of the 205 weather stations exhibited a statistically significant upward trend in daily maximum temperature and number of hours without precipitation. In contrast, the majority of daily precipitation exhibited a statistically significant downward trend. Unlike the unidirectional trend observed in daily maximum temperature or daily precipitation, daily minimum temperature and daily evapotranspiration presented a spectrum of behaviors, including instances of no discernible, upward and downward trends. Despite the varied outcomes in the analysis of daily minimum temperature and daily evapotranspiration, the overarching findings of the MK test indicated an overall reduction in daily precipitation and an increase in both maximum daily temperature and number of consecutive hours without precipitation across the Brazilian Atlantic forest. This suggests a scenario in which the ecosystem may encounter drier conditions in the future.
It is noteworthy that aridity conditions, reflective of short-term extremes, could not be adequately captured through statistics based on monthly values of precipitation, evapotranspiration or even AI. As we evaluated hourly data for maximum temperature and consecutive hours without precipitation reveals that a significant portion of the Brazilian Atlantic forest is already undergoing dry conditions.
In an attempt of establishing a vulnerability ranking, the outcomes of the meteorological indicators were synthesized and organized in Table 1. The ranking reflects the ascending order of vulnerability, delineating the weather stations in terms of their susceptibility to drought events within the Brazilian Atlantic Forest. There is no significant correlation between the assigned rank numbers and the latitudinal positions and elevation of the weather stations (Figure 4. This observation suggests that neither geographical location, as represented by latitude, nor elevation play a significant role in influencing the trends of dryness observed at each weather station.

4. Conclusions

The findings of this study provide significant insights into the spatial-temporal dynamics of drought in the Brazilian Atlantic forest ecosystem. The consistent occurrence of extreme monthly precipitation values across various weather stations suggests that they are a recurring phenomenon in the Brazilian Atlantic forest. However, in spite of the regular incidence of extreme monthly precipitation, the findings from the Mann-Kendall (MK) test demonstrate a prevailing decrease in daily precipitation alongside an elevation in both maximum daily temperature and the duration of consecutive hours without precipitation throughout the Brazilian Atlantic Forest. Additionally, the vulnerability ranking synthesized from the outcomes of the meteorological indicators does not show a significant correlation with the latitudinal positions and elevation of the weather stations, which implies that geographical location and elevation do not significantly influence the trends of dryness observed at each weather station. This observed trend hints at a prospective scenario wherein the ecosystem is likely to face drier conditions, all the while maintaining a consistent range in monthly precipitation values. It aligns with the research conducted by [12], which also highlighted the vulnerabilities of the Brazilian Atlantic forest to climate change.

Author Contributions

Conceptualization, Chaves, M.B., Rivera, C. and Farias Pereira, F.; methodology, Rivera, C. and Farias Pereira, F.; formal analysis, Chaves, M.B., Cavalcante, N. and Farias Pereira, F.; investigation, Chaves, M.B., Cavalcante, N. and Farias Pereira, F.; writing—original draft preparation, Chaves, M.B. and Farias Pereira, F.; writing—review and editing, Chaves, M.B., Rivera, C. and Farias Pereira, F.; visualization, Chaves, M.B.; funding acquisition, Farias Pereira, F. All authors have read and agreed to the published version of the manuscript.

Funding

We are grateful to Fundação de Amparo à Pesquisa do Estado de Alagoas (FAPEAL) for the travel grant offered to the authors through ERC – Fapeal/Confap/CNPq 2022 Call – Research opportunities in Europe for active PhD researchers from Brazil, which could enrich the work by presenting its bottom line and discussing its outcomes with researchers and peers from all over the world in seminars at Lund University, Sweden.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Weather stations localization
Figure 1. Weather stations localization
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Figure 2. Boxplots of accumulated monthly precipitation for all 205 automatic weather stations in the Brazilian Atlantic forest.
Figure 2. Boxplots of accumulated monthly precipitation for all 205 automatic weather stations in the Brazilian Atlantic forest.
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Figure 3. Spatial distribution of detected trend in minimum air temperature, maximum air temperature, aridity index, evapotranspiration, precipitation, and consecutive hours without precipitation by weather station.
Figure 3. Spatial distribution of detected trend in minimum air temperature, maximum air temperature, aridity index, evapotranspiration, precipitation, and consecutive hours without precipitation by weather station.
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Figure 4. Scatter plots illustrating the relationship between latitude and elevation against the order of the weather station in the ranking of vulnerability to drought events. The black solid line represents the linear regression model fitted to the data.
Figure 4. Scatter plots illustrating the relationship between latitude and elevation against the order of the weather station in the ranking of vulnerability to drought events. The black solid line represents the linear regression model fitted to the data.
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Table 1. A vulnerability ranking for weather stations presented in ascending order according to their susceptibility to drought events within the Brazilian Atlantic Forest.
Table 1. A vulnerability ranking for weather stations presented in ascending order according to their susceptibility to drought events within the Brazilian Atlantic Forest.
Station NDD NWD AI Trend in ET Trend in Tmax Trend in NCDH Rank
A554 22 8 0.31 9.784 21.125 0.492 1
A752 27 3 0.40 3.016 3.613 0.616 2
A533 22 9 0.72 6.601 10.564 0.561 3
A455 19 11 0.28 8.297 6.572 0.517 4
A874 21 10 0.78 6.372 6.132 0.770 5
A555 21 9 0.19 2.827 3.102 0.565 6
A531 19 11 0.37 6.581 6.699 0.487 7
A529 19 11 0.72 12.163 12.430 0.496 8
A704 21 9 0.44 9.543 10.455 -0.227 9
A876 20 10 0.69 6.708 6.506 0.519 10
A631 18 13 0.57 9.400 5.845 0.587 11
A816 21 10 0.64 6.783 5.626 0.453 12
A527 20 10 0.54 4.666 4.580 0.488 13
A621 22 8 0.39 3.003 4.029 0.413 14
A734 19 11 0.59 6.771 8.050 0.426 15
A632 18 12 0.59 5.988 3.571 0.595 16
A634 26 4 0.04 -0.064 0.347 0.599 17
A735 20 11 0.55 3.143 6.924 0.454 18
A557 17 13 0.53 1.860 13.693 0.590 19
A615 22 9 0.68 3.725 2.800 0.481 20
A444 18 13 0.28 6.937 3.985 0.479 21
A727 19 12 0.50 3.146 6.724 0.455 22
A622 17 13 0.55 4.953 4.225 0.605 23
A835 21 9 0.83 2.541 3.327 0.567 24
F501 24 7 0.35 1.055 -0.468 0.563 25
A552 18 12 0.34 1.336 5.535 0.561 26
A513 23 8 0.49 1.652 2.766 0.458 27
A617 18 13 0.63 5.477 6.011 0.499 28
A633 18 12 0.56 3.300 0.589 0.622 29
A733 25 6 0.16 1.172 2.341 0.360 30
A344 20 10 0.42 1.625 7.621 0.193 31
A818 20 11 0.78 5.122 8.088 0.295 32
A716 21 9 0.73 2.819 5.790 0.307 33
B803 16 15 0.85 8.013 10.117 0.580 34
A304 22 9 0.19 0.593 4.076 0.256 35
A858 18 13 0.96 6.904 7.064 0.492 36
A884 21 10 0.77 1.413 -1.292 0.677 37
A743 19 12 0.59 1.562 1.022 0.610 38
A530 17 13 0.63 8.100 7.903 0.316 39
A657 24 6 0.15 -0.743 -2.005 0.491 40
A509 19 12 0.61 5.506 6.322 0.159 41
A864 16 14 0.77 6.019 5.586 0.572 42
A434 21 9 0.30 -0.043 -0.243 0.457 43
A521 18 12 0.81 2.845 5.508 0.497 44
A514 16 14 0.72 5.565 6.682 0.515 45
A011 18 11 0.60 1.972 6.513 0.342 46
A859 17 13 1.23 6.082 6.210 0.579 47
A846 17 14 1.29 9.931 8.324 0.534 48
A869 16 15 0.80 6.755 7.496 0.517 49
A768 19 12 0.42 -0.903 -0.851 0.610 50
A875 18 13 1.33 6.840 6.071 0.519 51
A502 18 13 0.67 6.714 6.462 0.195 52
A556 19 12 0.45 -2.268 1.676 0.572 53
A636 20 10 0.35 -2.310 -3.657 0.564 54
A845 20 10 1.00 2.049 3.050 0.467 55
A410 15 16 0.73 6.889 13.642 0.465 56
A627 22 9 0.55 -0.827 -3.505 0.528 57
A407 16 15 0.48 4.552 7.147 0.351 58
A709 22 8 0.32 -1.305 1.845 0.240 59
A518 20 10 0.45 0.886 0.189 0.386 60
A612 21 9 0.86 1.791 2.235 0.385 61
A630 20 10 0.43 -2.644 -4.861 0.566 62
A862 17 13 1.12 4.609 4.799 0.557 63
A614 20 10 0.43 -1.344 1.068 0.429 64
A880 18 12 1.07 3.388 3.295 0.515 65
A620 18 12 0.51 1.760 0.960 0.465 66
A613 20 11 0.41 -2.102 -1.265 0.497 67
A749 18 12 0.68 -0.742 1.263 0.602 68
A652 19 11 0.57 1.117 2.219 0.403 69
A755 18 12 1.29 2.837 2.914 0.581 70
A659 22 9 0.71 -2.382 -4.458 0.579 71
A602 19 12 0.72 3.200 4.103 0.224 72
A623 19 11 0.70 -0.788 -0.448 0.583 73
A819 18 12 0.76 2.361 4.858 0.315 74
A625 20 11 0.75 0.139 -1.269 0.558 75
A610 18 12 0.87 3.443 4.687 0.310 76
A866 15 15 1.04 1.839 7.543 0.650 77
A667 20 10 0.64 -4.085 -5.136 0.607 78
A763 16 15 0.78 3.434 1.801 0.610 79
A894 15 15 1.05 4.625 3.680 0.646 80
A626 20 11 0.76 0.130 -1.532 0.558 81
A823 17 13 1.43 3.169 3.622 0.588 82
A706 20 11 0.66 0.708 2.212 0.323 83
A301 16 14 0.51 1.334 12.855 0.303 84
A861 18 12 1.16 3.617 2.196 0.494 85
A618 20 10 0.46 -0.096 -0.981 0.338 86
A628 21 10 0.65 -2.927 -6.258 0.552 87
A355 17 14 0.43 2.012 4.467 0.274 88
A601 19 11 0.55 2.219 0.827 -0.096 89
A616 20 11 0.66 -1.960 2.470 0.396 90
A824 20 10 0.64 0.198 1.629 0.291 91
B806 17 14 0.88 2.114 1.102 0.605 92
A817 17 13 1.37 2.904 4.448 0.543 93
A841 14 17 1.01 8.740 12.219 0.469 94
A740 18 12 1.01 2.118 3.124 0.450 95
A837 20 11 1.20 1.579 2.699 0.457 96
A515 18 13 0.79 2.730 4.585 0.264 97
A637 21 10 0.60 0.195 -1.316 0.295 98
A414 15 15 0.48 3.229 3.956 0.330 99
A451 14 16 0.54 3.213 4.812 0.389 100
A532 17 14 0.46 0.419 0.848 0.503 101
A851 17 13 1.15 1.618 2.798 0.585 102
A417 14 17 0.77 6.709 9.262 0.355 103
A741 16 14 1.04 3.862 5.197 0.442 104
A035 16 15 0.64 2.800 6.656 0.248 105
A550 16 15 0.86 1.649 4.998 0.531 106
A701 18 12 0.81 0.644 3.687 0.362 107
A873 19 11 0.98 -4.112 -2.063 0.622 108
A566 14 16 0.77 3.761 -0.169 0.587 109
B804 17 14 1.14 1.723 1.482 0.613 110
A438 16 14 0.52 -0.188 5.500 0.373 111
A860 15 16 1.19 6.704 6.617 0.451 112
A721 18 13 0.53 1.664 0.847 0.250 113
A603 20 11 0.60 1.386 -1.701 0.012 114
A524 15 16 0.46 1.506 3.518 0.421 115
A744 17 13 0.44 -6.271 -4.955 0.587 116
A849 9 21 1.01 7.824 8.805 0.512 117
A870 17 14 0.89 1.550 -1.348 0.591 118
A511 12 18 0.84 4.703 7.364 0.444 119
A850 12 18 1.45 5.874 8.729 0.529 120
A517 17 13 0.77 0.216 2.103 0.457 121
A303 14 16 0.35 2.866 3.502 0.153 122
A510 13 17 1.06 5.528 8.611 0.380 123
A865 14 16 1.00 1.937 1.806 0.640 124
A619 19 12 0.99 2.564 0.592 0.233 125
A522 17 13 0.57 -1.720 -1.237 0.491 126
A863 12 19 1.01 3.441 2.705 0.625 127
A728 19 11 0.86 -2.993 -2.883 0.497 128
A750 8 23 0.97 4.312 4.020 0.647 129
A765 18 12 0.91 -1.363 -6.509 0.584 130
A540 18 12 0.75 -1.258 -1.049 0.448 131
A867 14 15 1.07 0.270 2.669 0.667 132
A855 14 17 1.27 7.278 6.364 0.400 133
A843 17 13 1.24 1.805 1.277 0.494 134
A769 18 12 0.71 -3.805 -4.196 0.503 135
A624 13 18 0.58 0.710 1.238 0.587 136
A707 15 15 1.26 6.620 8.099 0.089 137
A406 16 15 0.52 2.129 1.537 0.235 138
A352 10 20 0.91 1.349 8.241 0.576 139
A570 17 14 0.69 -1.242 -3.115 0.565 140
A456 NA NA NA 2.593 1.548 0.541 141
A712 19 12 1.00 -3.146 1.676 0.414 142
A840 19 12 1.24 -0.178 -0.172 0.474 143
A814 13 17 1.60 2.773 2.852 0.627 144
A606 12 18 0.66 1.205 12.149 0.342 145
A821 14 16 0.80 1.816 3.084 0.442 146
A431 13 18 0.60 8.213 -1.750 0.378 147
A607 15 15 0.91 1.247 4.111 0.421 148
A446 8 22 1.08 4.987 5.122 0.530 149
A810 20 10 0.82 -4.139 -5.149 0.344 150
A815 8 22 0.84 1.737 2.952 0.625 151
A409 14 17 0.75 0.919 11.779 0.247 152
A413 14 17 0.51 1.654 2.066 0.298 153
A609 15 15 0.89 0.522 1.894 0.482 154
A713 13 18 1.15 3.582 4.669 0.429 155
A322 16 14 0.37 -4.627 -0.834 0.388 156
A883 16 14 1.18 -0.549 -1.582 0.621 157
A882 13 17 1.08 1.119 -0.040 0.676 158
A751 11 19 1.40 5.840 4.555 0.487 159
A447 11 20 0.59 1.967 2.493 0.433 160
A897 18 13 1.52 -2.877 -4.832 0.681 161
A549 8 22 1.11 3.178 3.598 0.567 162
A356 18 12 0.55 -5.689 -5.749 0.272 163
A771 15 15 1.15 2.087 -2.456 0.550 164
A357 14 16 0.63 -5.420 -2.979 0.591 165
A868 16 14 1.32 -2.160 -2.248 0.712 166
A844 10 20 1.27 3.615 3.351 0.494 167
A839 13 18 0.79 2.736 2.453 0.308 168
A895 16 14 1.30 0.451 -1.966 0.528 169
A611 17 14 0.91 -2.020 -0.016 0.393 170
A421 12 18 0.76 -0.781 7.679 0.306 171
A857 9 22 1.54 3.271 4.571 0.501 172
A736 9 22 1.55 7.815 9.211 0.246 173
A871 13 18 1.10 1.922 1.729 0.481 174
A762 10 20 1.04 0.951 0.296 0.635 175
A807 10 20 1.26 5.506 4.792 0.343 176
A405 10 20 1.09 2.692 6.280 0.344 177
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