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than the MIA in both sunny and shaded locations, with a |
standard deviation of 78F in sunny and 88F (4.48C) in shaded |
locations. iButtons show that the 1088F threshold (shown by |
the horizontal line in Fig. 3c) is exceeded at some locations |
even for low values of the MIA heat index. At MIA heat index values greater than 1008F (37.88C) (which is close to the |
95% value for a heat index over the entire period), almost |
all iButton sites exceeded the 1088F threshold. The 1088F |
threshold criteria have only been met 14 times over the last |
70 years based on data at MIA (Fig. 4a). Since we know that |
iButton data often exceed this threshold, we can model the |
number instances of where this threshold would have been exceeded. We use the regression lines shown in Fig. 3c to calculate a “modeled” iButton average heat index (see methods, |
section 2). Figure 4 also shows that the number of days in excess of 1088F heat index occurs nearly 1=3 of the year at the |
iButton sensors. There is a trend of days in excess of 1088F |
heat index increasing 5.7 days decade21 |
. |
4. Conclusions and discussion |
This study uses hyperlocal data collected with citizens in |
Miami–Dade County to characterize hyperlocal urban heat |
exposure. We find that while minimum temperatures at sites |
within the county are well-represented by measurements at |
MIA, maximum temperature throughout the county were well |
in excess of MIA measurements. The heat index computed |
for the subset of iButtons that had humidity measurements exceed the threshold level (1088F) for heat advisories that is used |
by the National Weather Service for nearly one-third of the |
year, with a trend of approximately 6 more days per decade. |
While we used only the threshold level to indicate exceedances, and not duration (2 h1), these data indicate that extreme |
heat exposure is both a persistent and increasing issue in the |
county. This trend is, of course, an oversimplification since it |
assumes that the overall relationship between MIA and the |
county remains constant with time. The county has significantly |
urbanized over time with less greenspace and more impermeable surface (Miami–Dade County Open Data Hub 2021), |
which would suggest an increasing influence of urbanization on |
866 JOURNAL OF APPLIED METEOROLOGY AND CLIMATOLOGY VOLUME 62 |
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heat exposure over time and in the localized areas of our observations. As the degree of urbanization intensifies with expansion toward the west, we would expect that differences between |
the airport and the urban area would likely decrease. |
We interpret differences between maximum temperatures in |
the iButtons and MIA as representing meaningful differences |
in temperatures recorded by the sensors. The NWS Automated |
Surface Observing Systems (ASOS) instrument at the airport is |
located at the southwest corner of the Miami airport (well outside the footprint of urban Miami), placed at 2 m above the |
ground and is well ventilated with no buildings or structures in |
the immediate area. The iButtons are requested to be placed |
under cover, either in treed (with canopy) or open canopy |
(sunny) locations and are generally placed at 0.5–2-m height. A |
number of factors likely contribute to the overall higher maximum temperatures recorded by iButtons. Hyperlocal conditions |
such as proximity to ground surface, greenness, and permeable/ |
impermeable surfaces have been shown to impact the maximum |
temperatures in urban environments (Schwaab et al. 2021), and |
likely contribute to the variation we observed (Fig. 3). These |
site-to-site differences contain important information about |
heat exposure that is relevant to the impacts that residents experience in their daily lives. We expect we did not see large differences among “sunny” and “shady” conditions in this analysis |
simply because variation among more specific microenvironmental conditions requires further analyses. A forthcoming |
study will evaluate the influence of site characteristics on siteto-site differences. |
It is no surprise that there is generally higher potential heat |
exposure in urban areas of Miami, particularly in the warm |
season. The question is how hot is too hot? The choice of local or regional threshold to reveal extreme heat is generally |
based on a statistical approach, such that conditions are only |
rarely exceeded (Robinson 2001; Zhang et al. 2012; McElroy |
et al. 2020). The NWS advisory level of 1088F used in Miami– |
Dade County is a statewide metric based on heat-related emergency room admissions in select counties across the state. NWS |
offices do have discretion about issuing advisories, and forecasters use available data and models to evaluate whether |
an advisory should be issued (R. Molleda 2023, personal |
communication). However, this is a subjective decision, and |
there is a lack of available quantitative data to evaluate |
both the spatial extent and duration of possible excess heat |
exposure in parts of the forecast region. Our data can be |
used to help inform those decisions. Our results show that |
maximum heat index values are on average 118F higher than |
the airport. While the error attributed to some low-cost sensors should also be considered [;58F (2.88C)], this can be |
used as guidance for the overall (average) urban heat island |
effect in the county and indicates that localized areas of the |
county are at potentially near-dangerous levels throughout |
at least the warm season of the year (Fig. 4b). |
This finding also brings into question the concept of whether |
heat “spells” or “waves” are even an appropriate framework to |
assess human health impacts in this region. For example, simply |
lowering the threshold to a heat index of 1068F (41.18C) based |
on MIA would result in 56 heat advisories since 2000, and for |
1048F (408C) this would be 188, as compared with 7 days (or |
0.1%) for the 1088F threshold. The nonlinearity of the heat index makes the number of advisories extremely sensitive to the |
FIG. 2. The average maximum (top plot of each panel) and minimum (bottom plot of each panel) recorded temperature for the airport |
(black), iButton sensors in sunny locations (red), and iButton sensors in shaded locations (blue) for (a) September–October 2018, (b) June– |
December 2019, and (c) June 2020–January 2021. iButton data are only plotted for those days on which data were recorded. |
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choice of a single threshold. This may have the effect of increasing the number of heat advisories to a level where this becomes |
an ineffective communication or outreach tool, referred to by |
NWS as “warning fatigue.” Alternatively, if we choose a locally |
defined 95th percentile of MIA heat index as the threshold for |
extreme heat, as is commonly done (Turek-Hankins et al. 2020), |
This value is 100.88F (38.28C) for the entire period from 1950 to |
2019, and 102.18F (38.98C) for the post-2000 period (which is |
warmer overall). In this case we get 1382 advisories of the |
whole period, and 409 since 2000. Again, these high numbers of threshold exceedances also become problematic for |
looking at extreme heat as happening in “waves” with a return to “normal” offering relief. Further, these criteria need |
to be reevaluated regularly as the climate warms and as local conditions that impact the urban heat island evolve |
(Hess and Ebi 2016; Issa et al. 2021; McKinnon et al. 2021). |
We therefore suggest, simply based on the heat data, that using a single threshold criterion for the entire state that includes |
such a wide range of climate zones such as Florida is not appropriate for characterizing the danger of heat exposure. It is further critical to recognize that this approach may miss heat |
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