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Impact of large wildfires on PM10 levels and human mortality in Portugal

Tarín-Carrasco, Patricia,Augusto, Sofia,Palacios-Peña, Laura,Ratola, Nuno,Jiménez-Guerrero, Pedro

Abstract

Uncontrolled wildfires have a substantial impact on the environment, the economy and local populations. According to the European Forest Fire Information System (EFFIS), between 2000 and 2013 wildfires burned up to 740 000 ha of land annually in the south of Europe, Portugal being the country with the highest percentage of burned area per square kilometre. However, there is still a lack of knowledge regarding the impacts of the wildfire-related pollutants on the mortality of the country's population. All wildfires occurring during the fire season (June–July–August–September) from 2001 and 2016 were identified, and those with a burned area above 1000 ha (large fires) were considered for the study. During the studied period (2001–2016), more than 2 million ha of forest (929 766 ha from June to September alone) were burned in mainland Portugal. Although large fires only represent less than 1 % of the number of total fires, in terms of burned area their contribution is 46 % (53 % from June to September). To assess the spatial impact of the wildfires, burned areas in each region of Portugal were correlated with PM10 concentrations measured at nearby background air quality monitoring stations. Associations between PM10 and all-cause (excluding injuries, poisoning and external causes) and cause-specific mortality (circulatory and respiratory) were studied for the affected populations using Poisson regression models. A significant positive correlation between burned area and PM10 was found in some regions of Portugal, as well as a significant association between PM10 concentrations and mortality, these being apparently related to large wildfires in some of the regions. The north, centre and inland of Portugal are the most affected areas. The high temperatures and long episodes of drought expected in the future will increase the probabilities of extreme events and therefore the occurrence of wildfires.

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Impac o la ge wild i es on PM10 le els and human mo ali y in Po ugal Pa icia Ta ín-Ca asco1, So ia Augus o2,3, Lau a Palacios-Peña1,4, Nuno Ra ola5, and Ped o Jiménez-Gue e o1,6 1Physics o he Ea h, Regional Campus o In e na ional Excellence (CEIR) “Campus Ma e Nos um", Uni e si y o Mu cia, Spain. 2EPIUni - Ins i u o de Saúde Pública, Uni e sidade do Po o, Po o, Po ugal 3Cen e o Ecology, E olu ion and En i onmen al Changes, Faculdade de Ciencias, Uni e sidade de Lisboa (CE3C-FC-ULisboa), Lisboa, Po ugal. 4Dep . o Me eo ology, Me eo ed, Almend icos, Spain. 54. LEPABE-Labo a o y o P ocess Enginee ing, En i onmen , Bio echnology and Ene gy, Facul y o Enginee ing, Uni e si y o Po o, Rua D . Robe o F ias, 4200-465 Po o, Po ugal. 6Biomedical Resea ch Ins i u e o Mu cia (IMIB-A ixaca), Spain. Co espondence: Ped o Jiménez-Gue e o ([email p o ec ed]) Abs ac . Uncon olled wild i es ha e a subs an ial impac on he en i onmen , he economy and local popula ions. Acco ding o he Eu opean Fo es Fi e In o ma ion Sys em (EFFIS), be ween he yea s 2000 and 2013 wild i es bu n abou 170,000-740,000 ha o land annually on he sou h o Eu ope (Po ugal, Spain, I aly, G eece and F ance). Al hough mos sou he n Eu opean coun ies ha e been impac ed by wild i es in he las decades, Po ugal was he mos a ec ed, ha ing he highes pe cen age o 5 bu ned a ea compa ing o i s whole e i o y. Fo his eason, i dese es a close a en ion. Howe e , he e is a lack o knowledge ega ding he impac s o he wild i e- ela ed pollu an s on he mo ali y o he popula ion. All wild i es occu ing du ing he i e seasons (June-July-Augus -Sep embe ) om 2001 and 2016 we e iden i ied and hose wi h a bu ned a ea abo e 1000 ha we e conside ed o he s udy. To assess he spa ial impac o he wild i es, hese we e co ela ed wi h PM10 concen a ions measu ed a nea by backg ound ai quali y moni o ing s a ions, p o ided by he Po uguese En i onmen Agency (APA). Associa ions10 be ween PM10 and all-cause (excluding inju ies, poisoning and ex e nal causes) and cause-speci ic mo ali y (ci cula o y and espi a o y), p o ided by S a is ics Po ugal, we e s udied o he a ec ed popula ions, using Poisson eg ession models. Du ing he s udied pe iod (2001-2016), mo e han 2 million ha o o es we e bu ned in mainland Po ugal and he 48% o wild i es occu ed we e la ge i es. A signi ican co ela ion be ween bu ned a ea and PM10 ha e been ound in some NUTS III ( egions) on Po ugal, as well as a signi ican co ela ion be ween bu ned a ea and mo ali y. No h, cen e and inland o Po ugal a e he15 mos a ec ed a eas. The high empe a u es and long episodes o d ough expec ed on he u u e will inc ease he p obabili ies o ex eme e en s and he e o e, he occu ence o wild i es. 1 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. 1 In oduc ion The exis ence o wild i es cons i u es a conside able impac on he en i onmen and humans li ing in nume ous egions wo ld- wide. Clima e change has la ely been iden i ied as a e y impo an a iable o be conside ed in his ma e and global wa ming20 scena ios a e o ecas ing an inc ease o he numbe and in ensi y o wild i es du ing he nex yea s (Bowman e al., 2017). Global wa ming will p oduce changes in empe a u e and p ecipi a ion pa e ns which will inc ease he p e alence and se e i y o wild i es (Se ele e al., 2015), consequen ly impac ing u u e ai quali y (Schä e al., 2004). In ac , an inc ease on he numbe o d ough s, hea wa es and d y spells is sugges ed by clima e change p ojec ions, which could no only ex end he bu n a ea in ch onically impac ed a eas, bu also a ec new ones (Gille e al., 2004), as was he case o Sweden in he summe 25 o 2018 (Lidskog e al., 2019). One o he a eas o he wo ld mos us iga ed by wild i es is he Medi e anean basin (Po ugal being he mos impac ed coun y), which needs o be s udied ca e ully o add ess he conce ns o local popula ions. Al hough he e has been a sligh dec easing end in he bu n a ea in his egion since 2000 a e an inc easing pe iod in he p e ious 20 yea s (Eu opean En i onmen , Agency, h ps://www.eea.eu opa.eu/da a-and-maps/indica o s/ o es - i e-dange -3/ assessmen ), ecen ex eme e en s like he 2017 i es in Po ugal and he 2018 i es in G eece which e en esul ed in a se e e30 loss o human li es a e con i ming he wo s p ojec ions. In ac , a ecen s udy by Tu co e al. (2019) showed a ela ionship be ween d ough and he occu ence o wild i es and sugges ed an inc ease o bo h due o u u e clima e change. Bu al eady some yea s be o e, he PESETA (P ojec ion o Economic impac s o clima e change in Sec o s o he EU based on bo om-up Analysis) s udy es ima ed an inc ease o he bu n a ea in sou he n Eu ope in he u u e (Cisca e al., 2014). Uncon olled wild i es emi nume ous pollu an s de i ed om he incomple e combus ion o biomass uel, which cause35 damage o human heal h, pa icula ly he espi a o y sys em (Wo ld Heal h O ganiza ion, 2010). Examples include pa icu- la e ma e (PM), ca bon monoxide, me hane, ni ous oxide, ni ogen oxides, ola ile o ganic compounds (VOCs), and o he seconda y pollu an s (Cascio, 2018) ha a e eleased mainly in o he a mosphe e bu can be anspo ed o many o he en- i onmen al compa men s. Mo eo e , hey can a ec he physicochemical p ope ies o he a mosphe e, as o ins ance he in e ac ion o PM wi h sola adia ion which can p omp a modi ica ion o he empe a u e depending on he cha ac e is-40 ics o he ae osol (T en mann e al., 2005). Consequen ly, some o hese chemicals a e egula ed by he Eu opean Di ec i e 2008/50/EC o 21 May 2008 o he Eu opean Pa liamen and o he Council on Ambien Ai Quali y and Cleane Ai o Eu ope, which es ablishes h eshold alues o a sa e ai quali y. Bu al hough wild i e emissions a e a c ucial pa ame e o he local ai quali y (Kno e al., 2016), whe e in some cases he e a e al eady ch onically-exposed popula ions due o he e- quency and dimension o he e en s, hey a e no con ained by poli ical bo de s and can also a ec a eas a om he igni ion45 poin s due o he a mosphe ic anspo o he pollu an plumes. A numbe o s udies (e.g. Lin e al. (2012); Im e al. (2018); Liang e al. (2018); Augus o e al. (2020), among o he s) epo he in luence o na u al and an h opogenic emissions on ai quali y composi ion ac oss di e en coun ies, especially PM and oposphe ic O3. Fo wild i es i is also impo an o ake in o accoun some ac o s which in luence he plume dispe sion, such as he du a ion and space e olu ion o he i e e en and he me eo ological condi ions associa ed (Laza idis e al., 2008). An inc ease o ca dio ascula and espi a o y mo bidi y and50 mo ali y a e some o he impac hese con aminan s can ha e on humans (Johns on e al., 2012; Ta ín-Ca asco e al., 2019). 2 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. Fo ins ance, he e is a s ong e idence o he ela ionship be ween PM in gene al and mo ali y, especially om ca dio ascula diseases, o bo h long- e m and sho - e m exposu e (Ande son e al., 2012). Al hough some s udies co obo a e he exis ence o a link be ween he exposu e o wild i e- ela ed ai pollu an s and hospi al admissions, isi s o eme gency clinics o e en espi a o y mo bidi y (Liu e al., 2015; Reid e al., 2016), he impac s on human heal h a e di icul o quan i y and he eal55 e ec s s ill poo ly known. Rega ding PM, a ecen s udy ocusing on 10 sou he n Eu opean ci ies e ealed ha ca dio ascula and espi a o y mo ali y associa ed o PM10 (pa icles wi h ae odynamic diame e below 10 µm) was highe on days a ec ed by wild i es’ smoke han in smoke- ee days (Faus ini e al., 2015). The au ho s also ound ha PM10 om o es i es inc eased mo ali y mo e han PM10 om o he sou ces. So, he es ima ion o mo ali y due o exposu e o wild i e-gene a ed pollu an s is key o60 manage heal h esou ces and he necessa y public unds owa ds p e en ion and emedia ion, se ing up app op ia e policies and p o ocols (Rappold e al., 2012). The wo main ac o s o ake in o accoun o he wild i e’s e ec s a e he loca ion and, mos impo an ly, he size o he i e e en (cha ac e ised by he espec i e bu n a ea). When he wild i e occu s close o a la ge conu ba ion, he popula ion exposed is highe . Bu as Anali is e al. (2012) showed in hei s udy, small i es do no seem o ha e an e ec on mo ali y, whe eas65 medium and la ge episodes (wi h bu n a eas >1000 ha) ha e a signi ican impac on human heal h, which inc eases wi h he size o he i e. Aiming o enhance he knowledge on he e ec s o wild i es on human heal h, his s udy desc ibes he pa e n o wild i es in Po ugal o 16 yea s (2001-2016) and assesses he impac o hose e en s on he coun y’s popula ion mo ali y du ing he i e season (June, July, Augus and Sep embe ). In his wo k, he ocus is placed on indi ec e ec s o pollu an s emi ed by wild i es, namely assessing he in luence o wild i e-gene a ed PM10 on he Po uguese popula ion mo ali y. The70 ela ionship be ween he size o he wild i e (cha ac e ised by he espec i e bu ned a ea) and PM10 and his same pollu an and mo ali y has been s udied. The Nomencla u e o Te i o ial Uni s o S a is ics (NUTS) le el 3 (NUTS III) geog aphical di ision has been used o be able o compa e he e ec s o he i es in di e en pa s o he coun y. Finally, mon hly dea hs due o all-cause (excluding inju ies, poisoning and ex e nal causes) and cause-speci ic mo ali y (ca dio ascula and espi a o y) o all ages o each NUTS III has been s udied. These causes ha e been selec ed due o hei well-known connec ion wi h ai 75 pollu ion. 2 Me hodology and da a In his s udy, he e ec s o sho - e m pollu an s exposu e due o wild i es on human mo ali y a e quan i ied. The o es i e pollu an emissions we e es ima ed o he pe iod 2001-2016 du ing he summe mon hs (June-July-Augus -Sep embe ) in Po ugal mainland (23 NUTS III and mo e han 10 million people). Fo his quan i ica ion, wo s eps ha e been ollowed.80 Fi s , an assessmen o he incidence, pa e ns and a ia ions o bu ned a ea on a la ge ime ame and spa ially in eg a ed by NUTS III was done on he le els o ai pollu an s. PM10 and bu ned a ea has been co ela ed h ough linea eg ession, while he mo ali y da a and PM10 was co ela ed wi h Poisson eg ession. Da a was p ocessed and o de ed by NUTS and by mon h and yea . Finally, he co ela ion be ween he pollu an s emi ed by o es i es, he wild i es bu ned a ea and he 3 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. di e en causes o mo ali y du ing he pe iod 2001-2016 o he summe mon hs was s udied. The s udy is ocused in PM85 since i is one o he main pollu an s emi ed by wild i es, which can inc ease PM concen a ions up o 50% and mo e (Laza idis e al., 2008). Mo eo e , he e is a clea ela ion wi h se e al e ec s on human heal h (including mo ali y), in pa icula wi h espi a o y and ci cula o y diseases (Kollanus e al., 2016; Reid e al., 2016; Liang e al., 2018). The e was no enough PM2.5 da a collec ed om he Po uguese ai quali y managemen ne wo k o es ablish a co ela ion (only 20 s a ions measu e PM2.5 in he mainland). Fo all hese easons his s udy is ocused on PM10.90 2.1 Ta ge a ea Wi h 89 015 km2(9.11 Mha) mainland Po ugal accoun s o o e 96% o he coun y’s a ea and hos s o e 10 million inhabi an s in he wes Ibe ian Peninsula (sou hwes e n Eu ope). Wi h he la ges u ban a eas along he wes A lan ic coas , pa icula ly a ound he capi al Lisbon mo e o he sou h and he second la ges ci y (Po o) in he no h (see Figu e 1,le ), he coun y has mos o i s moun ain anges in he no h, eaching 1993 m in Se a da Es ela. Al hough showing a Medi e anean95 clima e, his opog aphic display leads o a ious clima e pa e ns along he coun y, wi h inc easing empe a u e and dec easing ain all om no hwes o sou heas (Mo ei a e al., 2011; Oli ei a e al., 2017). In e ms o land co e , Figu e 1,le shows a p edominance o ag icul u e by 2015 (o e 50% and mainly in he sou h), ollowed by o es s and sh ublands, which comp ise 43% o he e i o y (mainly in he no h and sou hwes ). This allied wi h high empe a u es in he summe mon hs ep esen a po en ial i e haza d, which un o una ely has been o en e i ied almos e e y summe o many yea s.100 Figu e 1. (Le ) Land co e in mainland Po ugal in 2015 (Global Fo es Wa ch, h ps://www.global o es wa ch.o g; (Righ ) Mainland Po ugal NUTS III egions as included in his con ibu ion. 4 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. 2.2 Da ase s 2.2.1 NUTS III bounda y da a The a ge domain was di ided by NUTS (Nomencla u e o Te i o ial Uni s o S a is ics) le el 3 (Figu e 1, igh ) o Po ugal mainland. NUTS is a geocode s anda d o e e encing he subdi isions o coun ies o s a is ical pu poses de eloped by he Eu opean Union, and a e di ided in h ee le els, es ablished by each EU membe coun y. The bounda ies o he NUTS III105 iles om mainland Po ugal (in o al, 23) we e e ie ed om he Eu os a web page (h ps://ec.eu opa.eu/eu os a /web/gisco/ geoda a/ e e ence-da a/adminis a i e-uni s-s a is ical-uni s/nu s) wi h QGIS3 so wa e. The downloaded da a a e o he 14 Ma ch 2019 e sion a a 1:60 million scale. 2.2.2 Wild i es da a The wild i e da a, collec ed in he pe iod om 2001 and 2016, was ob ained om he Po uguese Ins i u e o Na u e Conse a-110 ion and Fo es s (h ps://www.icn .p /). Fo his s udy, o es i es occu ing in he mon hs o June, July, Augus and Sep embe 2001-2016 ( he mon hs wi h highes empe a u es and d ie condi ions when mo e han 65% o i es happened) wi h mo e han 1000 ha o o al bu ned a ea we e selec ed and conside ed la ge i es. In o al, he e we e 331 e en s unde ha ca ego y. This da a was di ided by mon h and yea and he espec i e mon hly and yea ly sums we e conside ed o each NUTS III le el egion. A e, Al o Tâmega, Tâmega e Sousa, Oes e, Médio Tejo and Alen ejo Li o al a e he NUTS III whe e la ge i es du ing115 he s udy pe iod we e no ound. 2.2.3 Pollu ion da a The in o ma ion a ailable on he le els o pollu an s was ob ained om he Po uguese En i onmen Agency ai quali y ne - wo k (h ps://quala .apambien e.p /quala /index.php), es ablished o moni o he concen a ions o pollu an s acco ding o he Eu opean Legisla ion equi emen s (Eu opean Di ec i e 2008/50/EC o 21 May 2008). The ne wo k is i egula ly sca e ed120 h oughou he coun y, wi h a s onge p esence in he mos popula ed a eas. The isola ion o pollu an emissions due o bu n biomass is qui e complica ed as i depends on pa ame e s, such as ege a ion ype, he wea he condi ions on he bu n momen o he con ibu ion o o he sou ces, among o he s. Fo his eason, in his s udy, backg ound s a ions (speci ically u ban, sub- u ban and u al backg ound) we e selec ed, so ha he di ec impac o o he u ban and indus ial sou ces such as oad a ic, building hea ing and manu ac u ing combus ions was a oided. Conside ing all he pollu an s measu ed on he backg ound125 s a ions, PM was he one wi h a po en ially highe link o o es i es. And al hough some s a ions also measu ed PM2.5, he co e age was insu icien o d aw any signi ican co ela ions, so PM10 was chosen in he end. As o he wild i es da a, also he e he ime ange was om 2001 o 2016 and only he mon hs o June o Sep embe we e conside ed, wi h mon hly means used o he co ela ions. Concen a ions o PM10 we e ob ained o mainland Po ugal in all ypes o backg ound s a ions (a o al o 91 which co e 17 NUTS III, as shown in Figu e 2)- Gi en he une en co e age o he130 a ge domain, mos s a ions a e loca ed in he me opoli an a eas o Opo o (14 s a ions) and Lisbon (24 s a ions) and in he 5 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. es o he coas al a eas, whe e he highe popula ion (NUTS III commonly abo e 250,000 inhabi an s, Figu e 2) demands a igh e con ol o he ai quali y, bu whe e, in u n, no a lo o la ge wild i es occu due o he u banized land use. Figu e 2. Popula ion o each NUTS III acco ding o he 2011 Census (h ps://www.ine.p ) and espec i e numbe o moni o ing s a ions o PM10. 2.2.4 Mo ali y da a Mo ali y da a co e ing he pe iod om 2001 o 2016 was ob ained om S a is ics Po ugal (h ps://www.ine.p ). Mon hly135 dea h coun s due o all-cause (In e na ional Classi ica ion o Diseases (ICD-10), codes A00-R99) excluding inju ies, poisoning and ex e nal causes; and cause-speci ic mo ali y: ca dio ascula (codes I00-I99) and espi a o y (J00-J99) we e collec ed o each NUTS III egion o Po ugal, comp ising all-age esiden s. These mo ali y causes we e selec ed since hey ha e been epo ed p e iously in li e a u e as impo an in hei connec ion wi h ai pollu ion (Hoek e al., 2013; Liu e al., 2015; Kollanus e al., 2016; Münzel e al., 2018), in pa icula wi h pa icula e ma e (PM). O he ele an mo ali y causes, such as Ch onic140 Obs uc i e Pulmona y Disease (COPD, codes J40-J45) and as hma (ICD-10, code J47), we e also conside ed, howe e he educed numbe o dea hs due o hese diseases in he s udy pe iod p e en ed he es ablishmen o co ela ions. 6 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. 2.3 S a is ical analysis 2.3.1 Co ela ions be ween PM10 and bu ned a ea Co ela ions be ween PM10 and he o al bu ned a ea pe mon h by NUTS III we e es ima ed using Pea son co ela ions145 coe icien s (Pea son and Gal on, 1895). Pea son co ela ion is used o co ela e wo con inuous a iables ha ing a no mal dis ibu ion, while Poisson coe icien s a e used o co ela e a coun a iable wi h a con inuous a iable. These me hodologies a e widely used in s udies co e ing he opic o heal h impac s o ai pollu ion (e.g. Islam and Chowdhu y (2017); Palla és e al. (2019); Rahman e al. (2019); Ro i a e al. (2020); among many o he s). Resul s we e conside ed s a is ically signi ican i he p- alue was p<0.05. Co ela ions we e pe o med using he de ended da a se ies o bu ned a ea and PM10 in o de o emo e150 he s ong seasonal cycle o hese a iables and a oid spu ious co ela ions. The de ending me hod ollows Ta ín-Ca asco e al. (2019), using he i s - ime di e ence ime se ies. 2.3.2 Associa ions be ween bu n a ea, PM10 and mo ali y The associa ions o mon hly a e age PM10 le els, and he size o he wild i es (bu n a ea >1000 ha and bu n a ea <1000 ha) wi h mean mon hly mo ali ies (all-cause, espi a o y and ca dio ascula causes) we e s udied o he mon hs June, July, Augus 155 and Sep embe o he pe iod be ween 2001 and 2016. The e ec es ima es we e ob ained o each NUTS III egion using Pea son eg ession models. The esul s we e exp essed as he Rela i e Risk (RR) o all-cause, ca dio ascula and espi a o y mo ali ies wi h a 95% con idence in e al (95% CI). All eg ession models we e pe o med using IBM SPSS S a is ics 25.0 so wa e. 3 Resul s and discussion160 The esul s ob ained in he s udy a e p esen ed as ollows. Fi s , he desc ip ion o he si ua ion in Po ugal in e ms o geo- g aphical dis ibu ion o he bu ned a ea is p esen ed. Then, a summa y o he PM10 concen a ions du ing he summe mon hs o he yea s 2001-2016 is p esen ed. Finally, he co ela ions be ween bu ned a ea and PM10 and he po en ial associa ions o wild i e-de i ed PM10 and all-cause mo ali y is p esen ed in his sec ion. 3.1 Spa io- empo al pa e ns o wild i es165 3.1.1 Bu ned a ea F om 2001 o 2016 pe iod mo e han 2 million ha o o es we e bu ned in mainland Po ugal. A ound 48% due o la ge i es (>1000 ha). Du ing his pe iod, he wild i es occu ed on di e en a eas in Po ugal, as shown in Figu e 3. The no h, cen e and inland o Po ugal a e he a eas wi h he highes numbe o wild i es and he highes bu ned a ea, being Bei as e Se a da Es ela and Bei a Baixa. Also Lezí ia do Tejo (in Alen ajo) and Alga e (in he sou h) (Figu e 1) can170 be ound among he mos a ec ed a eas (in numbe o wild i es and bu ned a ea). As seen in Figu e 3, he no h and cen e o 7 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. Figu e 3. Bu ned a ea and numbe o i es (>1000 ha) pe NUTS III om June o Sep embe in he pe iod 2001-2016. Po ugal is whe e he mos ex ensi e o es s in he coun y (Nunes e al., 2019), pa icula ly abundan in pine and eucalyp us ees, wo species ha ha e been associa ed wi h ex eme wild i e e en s (Maia e al., 2014). Addi ionally, dense Medi e anean o es s o e ha d- o- each moun ains can also be ound in hese a eas, which combined enhance he di icul y o he i e igh ing e o s. The Alga e, which despi e being loca ed in he sou h coas , also has some moun ains wi h o es s, su ounded by a175 conside ably d y and a id e ain, especially in he summe (Nunes e al., 2019). Bei a Baixa is he egion which p esen ed he mos bu ned a ea du ing he pe iod 2001-2016, wi h almos 124,000 ha in o al. Bu Bei a e Se a da Es ela is he a ea whe e he highes numbe o wild i es was ound, 47 in o al. On he o he hand, Lezí ia do Tejo is he NUTS III egion mos a ec ed by wild i es, conside ing he numbe o la ge i es and bu ned a ea oge he . Oes e and A ea Me opoli ana de Lisboa a e he a eas wi h a smalle numbe o la ge i es, only one du ing he a ge ime ame (since hese a e mainly non- o es ed a eas).180 Table 1 p esen s an o e iew o he bu ned a ea and occu ences o la ge i es by NUTS III a eas in mainland Po ugal. On he o he hand, Table 2 shows he yea ly a iabili y du ing he s udied pe iod o he numbe o he occu ences and bu ned a ea. In 2008 no wild i es o e 1,000 ha o bu ned a ea occu ed, whe eas 2003 accoun ed o 81 o occu ences o la ge i es, which we e esponsible o 80% o he o al bu ned a ea in ha yea . The da a in Table 2 sugges s ha i is no possible o pe cei e a yea ly pa e n o wild i es in Po ugal ega ding he occu ences, bu ned a ea o he con ibu ion o la ge185 i es o he bu ned a ea, bu o he s udies ha e shown a ela ionship wi h high empe a u es and d ough pe iods (Tu co e al., 2019). 8 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. Table 1. To al bu ned a ea and occu ences o la ge i es by NUTS III a eas in mainland Po ugal in he pe iod 2001-2016 in he mon hs o June, July, Augus and Sep embe ( o al o 64 a ge summe mon hs). NUTS Mon hs wi h la ge i es (N) Numbe o la ge i es (N) To al bu ned a ea (ha) No h Al o Minho 7 14 53918 Cá ado 3 4 7731 A e 4 4 5410 Al o Tâmega 10 21 48415 Te as de T ás-os-Mon es 7 10 28050 A. M. Po o 5 8 40840 Tâmega e Sousa 4 4 5706 Dou o 14 27 48907 Cen e A ei o 3 6 17481 Viseu Dão-La ões 11 31 60744 Coimb a 8 16 45673 Bei as e Se a da Es ela 17 49 115503 Lei ia 6 13 28347 Médio Tejo 11 31 96947 Bei a Baixa 7 14 59032 Oes e 1 1 1700 A.M.Lisboa 1 1 2756 Alen ejo Leizí ia do Tejo 2 3 24404 Al o Alen ejo 4 12 70657 Alen ejo Cen al 3 6 1970 Alen ejo Li o al 3 5 16176 Baixo Alen ejo 2 2 9240 Alga e 9 19 107273 9 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. cen e and inland o Po ugal. Wild i es do no ollow a pa e n in numbe o he occu ences o size du ing he yea s s udied. These e idences we e ound despi e he di icul ies ha he une en sca e ing o he ai moni o ing s a ions analysing PM10 in Po ugal posed, since he a eas whe e wild i es a e usually mo e equen (inland) a e a om he u ban cen es (mainly275 along he coas ), and hus, no abundan in ai quali y da a a ailabili y due o he sho age (o e en lack in some NUTS III) o moni o ing s a ions. These egions also ha e an aged popula ion, poo e economy and less heal h ca e esou ces, which can lead o an inc ease in he mo ali y a es in gene al. The socio-economic s a us o he popula ion a ec ed and he heal h ca e acili ies and measu es exis ing in he communi ies ha e o be aken in o accoun (Oli ei a e al., 2017), adding o he coun less pa ame e s ha may a ec hese es ima ions which con ibu e o conside able gaps iden i ied in his ype o s udies (Black280 e al., 2017). Du ing he summe mon hs occu almos 30% o he dea hs o all diseases and ca dio ascula while o espi a o y diseases mo ali y is a ound a 26%, so we can conclude ha cold empe a u es a e in mo e esponsible o all cause dea hs han wa m ones. These episodes occu ed du ing he summe mon hs (June-July-Augus -Sep embe ), when high empe a u es and long285 episodes o d ough inc ease he p obabili ies o unde go one o hese ex eme e en s. On a u u e uled by clima e changes, he high empe a u es and long pe iods o d ough ha usually uel big i es a e expec ed o inc ease, hus leading he way o mo e ex eme and in ense e en s o occu , e en ou side he ypically a ec ed egions. Thus, mo e popula ion will be exposed mo e equen ly o high pollu an le els, a ec ing hei gene al heal h, and inc easing ch onic diseases and mo ali y. Hence, es ic i e policies and p o ocols o imp o e he e ec i eness o p e en i e and mi iga ion ac ions mus be en o ced o ace his290 en i onmen al and socie al issue. Da a a ailabili y. Da a is publicly a ailable h ough he websi es men ioned in he ex : –EFFIS (Eu opean Fo es Fi e In o ma ion Sys em). Da a and Se ices, 2019. A ailable a h ps://e is.j c.ec.eu opa.eu/applica ions/ da a-and-se ices/ (las accessed 11/10/2019). –ICNF (Ins i u o da Conse ação da Na u eza e das Flo es as), 2019. A ailable a h ps://www.icn .p /(las accessed: 01/09/2019).295 –INE (Ins i u o Nacional de Es a ís ica). S a is ics Po ugal - Web Po al, 2019. A ailable a : h ps://www.ine.p /xpo al/xmain?xpid= INE&xpgid=ine_indicado es&con ec o=pi&indOco Cod=0008273&selTab= ab0 (las accessed 16/10/2019). –GWF (Global Fo es Wa ch), 2020. A ailable a h ps://www.global o es wa ch.o g/map/?g w i es= ue (las accessed, 10/10/2020). –PORDATA (Base de Dados Po ugal Con empo âneo). População esiden e: o al e po g andes g upos e á ios (in Po uguese), 2019. A ailable a h ps://www.po da a.p (las accessed 31/03/2020).300 All he compiled da a is a ailable upon con ac ing he co esponding au ho ([email p o ec ed]) Au ho con ibu ions. PT-C w o e he manusc ip , wi h con ibu ions om SA and NR. The manusc ip was inally e ised by PJ-G. P-TC and SA designed he expe imen s and led he s a is ical analysis, wi h he suppo o LP-P, NR and PJ-G. 16 h ps://doi.o g/10.5194/nhess-2021-38 P ep in . Discussion s a ed: 12 Feb ua y 2021 c Au ho (s) 2021. CC BY 4.0 License. Compe ing in e es s. The au ho s decla e no con lic o in e es . Acknowledgemen s. The au ho s a e hank ul o he G-MAR esea ch g oup a he Uni e si y o Mu cia o he ui ul scien i ic discussions.305 Financial suppo . 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