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Performance of Low-Height Railway Noise Barriers with Porous Materials

Lázaro, João,Pereira, Matheus,Costa, Pedro Alves,Godinho, Luís

Abstract

Rail transport is the most sustainable transportation mode, with the lowest energy consumption and carbon footprint. However, the noise induced by railway traffic in urban regions is a significant drawback and several reports point out the risks and the amount of people suffering from direct exposure to railway noise. One of the most used mitigation measures for railway noise is the implementation of noise barriers. Although they offer a significant reduction in noise levels, their height makes people feel enclosed. Therefore, in the case of railway infrastructure, the solution to the problem may lie in the use of barriers with a lower height placed close to the railway track. As the noise-forming mechanisms are mainly located at the track level, placing the barrier in a position close to the track allows mitigating rail noise without causing the problems identified above for the population in the vicinity. The purpose of this paper is to illustrate the development of a barrier solution to be used in a railway context through numerical modelling with the Boundary Element Method (BEM). The solutions developed were placed close to the track and have a low height. The geometry was defined so as to direct the energy back to the track to take advantage of the acoustic properties of the ballast. The addition of a porous granular material on the inner face of the barrier allows the control of reflections between the vehicle body and the barrier, increasing its acoustic efficiency. Finally, considering the most efficient solution, the insertion loss in a network of receivers located 10 m away from the track is analysed in order to study the noise reduction levels in a place where human receivers are usually located.

Full text

  Ci a ion: Láza o, J.; Pe ei a, M.; Cos a, P.A.; Godinho, L. Pe o mance o Low-Heigh Railway Noise Ba ie s wi h Po ous Ma e ials. Appl. Sci. 2022,12, 2960. h ps://doi.o g/ 10.3390/app12062960 Academic Edi o : Massimo Ga ai Recei ed: 4 Feb ua y 2022 Accep ed: 3 Ma ch 2022 Published: 14 Ma ch 2022 Publishe ’s No e: MDPI s ays neu al wi h ega d o ju isdic ional claims in published maps and ins i u ional a il- ia ions. Copy igh : © 2022 by he au ho s. Licensee MDPI, Basel, Swi ze land. This a icle is an open access a icle dis ibu ed unde he e ms and condi ions o he C ea i e Commons A ibu ion (CC BY) license (h ps:// c ea i ecommons.o g/licenses/by/ 4.0/). applied sciences A icle Pe o mance o Low-Heigh Railway Noise Ba ie s wi h Po ous Ma e ials João Láza o 1,*,† , Ma heus Pe ei a 1,† , Ped o Al es Cos a 1,† and Luís Godinho 2,† 1CONSTRUCT, Facul y o Enginee ing (FEUP), Uni e si y o Po o, Rua D . Robe o F ias, 4200-465 Po o, Po ugal; [email p o ec ed] (M.P.); [email p o ec ed] (P.A.C.) 2ISISE, Depa men o Ci il Enginee ing, Uni e si y o Coimb a, Pólo II, Rua Luís Reis San os, 3030-788 Coimb a, Po ugal; [email p o ec ed] *Co espondence: jlaza [email p o ec ed] † These au ho s con ibu ed equally o his wo k. Abs ac : Rail anspo is he mos sus ainable anspo a ion mode, wi h he lowes ene gy con- sump ion and ca bon oo p in . Howe e , he noise induced by ailway a ic in u ban egions is a signi ican d awback and se e al epo s poin ou he isks and he amoun o people su e ing om di ec exposu e o ailway noise. One o he mos used mi iga ion measu es o ailway noise is he implemen a ion o noise ba ie s. Al hough hey o e a signi ican educ ion in noise le els, hei heigh makes people eel enclosed. The e o e, in he case o ailway in as uc u e, he solu- ion o he p oblem may lie in he use o ba ie s wi h a lowe heigh placed close o he ailway ack. As he noise- o ming mechanisms a e mainly loca ed a he ack le el, placing he ba ie in a posi ion close o he ack allows mi iga ing ail noise wi hou causing he p oblems iden i ied abo e o he popula ion in he icini y. The pu pose o his pape is o illus a e he de elopmen o a ba ie solu ion o be used in a ailway con ex h ough nume ical modelling wi h he Bounda y Elemen Me hod (BEM). The solu ions de eloped we e placed close o he ack and ha e a low heigh . The geome y was de ined so as o di ec he ene gy back o he ack o ake ad an age o he acous ic p ope ies o he ballas . The addi ion o a po ous g anula ma e ial on he inne ace o he ba ie allows he con ol o e lec ions be ween he ehicle body and he ba ie , inc easing i s acous ic e iciency. Finally, conside ing he mos e icien solu ion, he inse ion loss in a ne wo k o ecei e s loca ed 10 m away om he ack is analysed in o de o s udy he noise educ ion le els in a place whe e human ecei e s a e usually loca ed. Keywo ds: ailway noise; low heigh noise ba ie s; acous ic e iciency; noise mi iga ion 1. In oduc ion Railway anspo is he mos sus ainable mode o anspo , wi h he lowes ene gy consump ion and ca bon oo p in compa ed o any o he mode o anspo . Howe e , a epo by he Eu opean En i onmen Agency (EEA) [ 1 ] om 2019 on his subjec s a es ha a he Eu opean le el, ail noise is he second mos dominan sou ce, wi h an es ima ed 22 million people exposed o a leas 55 dB du ing he day and nigh pe iods. On he same subjec , howe e , wi h a di e en ime ho izon, he epo by he Eu opean En i onmen Agency [ 2 ], whose aim is o p ojec scena ios o he decade 2020 o 2030, s a es ha he si ua ion o he popula ion’s exposu e o en i onmen al noise le el in Eu ope will wo sen in p ac ically all a eas esponsible o cu en exposu e le els. The p ojec ions sugges ha in 10 yea s mo e han one million people will be exposed o excessi e ail noise, bo h in u ban cen es and ou side hese agglome a ions. In ligh o he abo e, a epo o he Wo ld Heal h O ganisa ion (WHO) Regional O ice o Eu ope [ 3 ] is p esen ed. This documen highligh s he e ec s o noise and inco po a es a numbe o indica ions o ce - ain policies ha mus be implemen ed in o de o ensu e heal h and well-being o people li ing wi h he mos di e se o ms o en i onmen al noise. The WHO wo king g oup s a e Appl. Sci. 2022,12, 2960. h ps://doi.o g/10.3390/app12062960 h ps://www.mdpi.com/jou nal/applsci Appl. Sci. 2022,12, 2960 2 o 18 ha , o he day ime pe iod, noise le els should be below 54 dB, and o he nigh - ime pe iod, hey should no exceed 44 dB. Finally, i s esses ha in e en ions o educe noise le els and o comply wi h he limi s indica ed should ocus on in e en ions a he ack le el, he imp o emen o olling s ock and he implemen a ion o small noise ba ie s. Rail noise mi iga ion measu es can be applied in h ee di e en loca ions and acco ding o he en i onmen and he le el o noise p essu e educ ion ha one wan s o achie e [ 4 ]. Usually, he mos widely deployed solu ions a e hose ha ac a he le el o he p op- aga ion pa h o a he le el o he ecei e s. In places whe e housing densi y is high, he solu ions ha ac on he pa h o p opaga ion a e mo e ad an ageous in economic e ms [ 4 ]. Acous ic ba ie s a e usually a i icial and solid elemen s made o di e en ypes o ma e ial and placed in di e en posi ions, depending on he place o be p o ec ed. This noise mi iga ion solu ion has been widely adop ed in he con ex o oad noise mi iga- ion, and he e a e se e al me hods o designing hese solu ions. Acous ic ba ie s can ha e di e en ope a ing p inciples depending on he ma e ial hey a e made o ; i.e., hey can wo k by e lec ing acous ic wa es and/o abso bing hem. In gene al, he ba ie s a e e ical elemen s be ween 3 m and 4 m high posi ioned along he oad o ailway. Howe e , despi e he inhe en bene i s o educing noise and imp o ing he quali y o li e o he popula ion li ing nea by, his ype o solu ion aces he eluc ance o he popula ions li ing nea he ailway in as uc u e. This si ua ion is ela ed o he size o he ba ie , a ec ing he ield o ision, causing a sense o imp isonmen , loss o na u al ligh o a ec ing ai ci cula- ion. F om ano he pe spec i e, o hose who a el on ains, complain s a e also egis e ed o simila easons [ 5 – 7 ]. In o de o ackle some o he nega i e poin s iden i ied o he highe acous ic ba ie s, namely, being obs acles o one’s ield o ision, he na u al e olu ion o hink- ing has led o he c ea ion o solu ions whose wo king p inciple is simila o he one in ended o be applied in he wo k p esen ed in his documen . The inhe en ad an age o low-heigh solu ions is ela ed o he posi ioning o his elemen . As he mechanisms o noise gene a ion a e mos ly a he le el o he ail [ 8 ], he placemen o he ba ie in a posi ion close o he ack allows he p opaga ion o sound wa es o be in e up ed close o he sou ce. The educed heigh o hese elemen s hus allows his posi ioning close o he sou ce wi hou cons i u ing an obs acle o he ield o ision o passenge s and passe s-by. Bea ing his in mind, se e al au ho s ha e wo ked on his issue in o de o de elop a so- lu ion o mi iga e he noise le els associa ed wi h ail a ic. The s udies om he li e a u e p esen solu ions o he design o he ba ie s and o a mo e e ec i e nume ical modelling. Koussa [ 9 ] s udied, bo h nume ically and expe imen ally, he use o gabion walls as a o m o mi iga ion. The esul s indica e ha his solu ion can achie e up o 8 dB(A) o inse ion loss. Jilibois [ 10 ] p esen s a ull-scale model o an L-shaped ba ie buil wi h wooden panels and inside wi h abso ben ib ous ma e ial. Tes s ca ied ou by he expe imen al au ho e ealed an a enua ion o 10 dB(A). Nieuwenhuizen [ 11 ] showed ha he Du ch cal- cula ion scheme o con en ional ba ie s is easonably applicable o low-heigh solu ions. Finally, Kasess [ 12 ] p oposes co ec i e unc ions ha allow one o e icien ly calcula e com- plex geome ies using BEM, in o de o apply mo e complex geome ies in noise mapping p og ams. To con ol he e lec ions be ween he ca body and he noise ba ie , an abso p- i e ea men is equi ed. Fibe s and oams a e commonly used in passi e noise con ol; howe e , o ex e nal applica ions, hese ma e ials equi e p o ec ion agains en i onmen al agen s and s uc u al ein o cemen . Because o hese equi emen s, he in e es in sound abso p i e solu ions, such as po ous conc e e, made using consolida ed ligh weigh and sus ainable g anula ma e ials ha e inc eased o e ecen decades [ 13 – 21 ]. The in es iga- ion o he luid-equi alen ep esen a ion o po ous conc e e made wi h expanded clay has been shown o be ele an in he scien i ic communi y. Ca bajo e al. [22] s udied pe o- a ed conc e e and highligh ed he highe du abili y and he excellen s eng h- o-weigh a io o his solu ion. Pe ei a e al. [ 23 ] s udied he in luence o he wa e –cemen a io, he expanded clay g ain size, and he sample hickness in he sound abso p ion beha iou , while Zolan a i [ 24 ] s udied he luid-equi alen ep esen a ion o po ous conc e e using di e en agg ega es. Appl. Sci. 2022,12, 2960 3 o 18 The modelling o he ailway scena io has, o he easons gi en, an impo an ole o play in o ecas ing and c ea ing measu es o mi iga e ail a ic-induced noise. The Bounda y Elemen Me hod (BEM) is widely used o sol e acous ic p oblems [ 7 , 25 ], and can be an excellen op ion o model he e ec o mi iga ion measu es. The e sa ili y o his nume ical me hod allows he c ea ion o simply e lec i e acous ic ba ie s and/o he inclusion o po ous ma e ial which ac s as a sound abso p ion elemen , allowing he im- p o emen o he pe o mance on he ba ie , mi iga ing he ene gy e lec ed be ween he ehicle and he ba ie . In his a icle, he BEM will be used o sol e an ex e nal acous ic p oblem, essen ially o es he geome y o he ba ie s. In addi ion, a BEM o mula ion conside ing mul iple ma e ial egions is implemen ed o allow he modelling o he e ec o possible abso p i e ma e ials coupled o he noise ba ie . Using his model, i becomes possible o model he abso p i e ma e ials using equi alen luid heo ies, leading o a ealis ic ep esen a ion o such media. To assess he capaci y o he ba ie , he inse ion loss was used, i.e., he di e ence be ween he scena io wi h and wi hou he ba ie . Using he inse ion loss allows he ba ie o be assessed as a noise con ol measu e placed in a lo- ca ion wi h speci ic cha ac e is ics. In his way, he IL calcula ion p esen s he ac ual losses o e a wide ange o equencies, o any se o ecei e s, ega dless o he scena io o be e alua ed and mainly ega dless o he ype o ma e ial and geome y o he p o o ype. This pape ’s s uc u e is as ollows: Sec ion 2shows he expe imen al ailway noise cha ac e isa ion. Sec ion 3p esen s he expe imen al p ocedu e used o cha ac e ise po ous conc e e samples, allowing he luid-equi alen heo y ep esen a ion. Sec ion 4 p esen s he nume ical o mula ion o he BEM used o model he desc ibed p oblem. Sec ion 5p esen s he s a egy used o de ine he ba ie ’s geome y and he pa ame ic s udy o di e en noise ba ie con igu a ions. Then, Sec ion 6shows he sound p essu e le els p edic ed a ound he noise ba ie , in he p esence o he ain, and he inse ion loss esul s. Finally, Sec ion 7summa ises he main conclusions o his wo k. 2. Railway Noise Cha ac e isa ion Noise induced by ail a ic has se e al sou ces wi h di e en cha ac e is ics. Despi e he a ious componen s o ailway noise, he noise gene a ed by he wheel- ail in e ac ion plays he mos impo an ole in noise gene a ion. The a iable ha mos condi ions he sound p essu e le els and he o igin o he noise is he unning speed o he ehicles as illus a ed in Figu e 1, whe e he main noise sou ces a e de ined acco ding o he ain speed. 10 20 50 100 200 300 400 Speed [km/h] 70 80 90 100 110 120 130 Sound P essu e Le el [db(A)] T ac ion noise Rolling noise Ae odynamic noise To al Figu e 1. E olu ion o he con ibu ion o he di e en sou ces acco ding o he speed o ci cula ion (adap ed om [26]). The comple e s udy o he ailway noise p oblem in ol es examining se e al dimen- sions, namely gene a ion, p opaga ion and ecep ion. The e o e, he de ini ion o measu es Appl. Sci. 2022,12, 2960 4 o 18 aimed a i s mi iga ion equi es a clea unde s anding o hese dimensions. Consequen ly, i can be concluded ha only he cha ac e isa ion o noise in di e en ypes o scena ios, wi h di e en unning speeds, ehicle ypes, ack ypes and u ban meshes allows a clea e iew o he noise le els in ol ed and especially which a ia ions a e associa ed wi h he di e en a ic condi ions men ioned abo e. In his con ex , he main objec i e o he expe imen al cha ac e isa ion is o cla i y he noise le els associa ed wi h he a ic unde analysis. The sys ema isa ion o maximum noise le els, as well as he equency con en in ol ed, ela ing hem o speci ic condi ions, makes i possible o be e de ine mi iga ion measu es o deal wi h he noise con en iden i ied. In his wo k, a cha ac e isa ion campaign has been pe o med, in which he acquisi ion o he signal was made using ou mic ophones Beh inge ype ECM 8000, connec ed o a Focus i e Scla e 4P e USB o he signal acquisi ion, as is shown in Figu e 2. Pos - p ocessing o he da a was pe o med in Ma lab using he ITA-Toolbox unc ions [ 27 ]. Figu e 2. Expe imen al se up o he acous ic signal acquisi ion; ( 1 ) Beh inge ECM 8000 mic ophone, (2) compu e , (3) Focus i e Scla e 4P e USB acquisi ion uni . The placemen o he mic ophones was de ined o allow acqui ing he noise in he clos- es possible place o he sou ce, and a successi ely la ge dis ances om he sou ce, hus allowing o s udy in a comple e way he p opaga ion o he sound wa es. Figu e 3shows he se up used o he measu emen , wi h he dis ance be ween mic ophones and posi ion ela i e o he ack. Figu e 4shows pho os aken a he measu emen si e, in scena ios wi h and wi hou ehicle, espec i ely. As can be seen om he illus a ions, he mic ophone called M1 is e y close o he sou ce, while he o he s, M2, M3 and M4, occupy a ela i e posi ion in acco dance wi h places whe e pedes ians ci cula e. Be o e each measu emen campaign, e i ica ion was pe o med making use o a BK 4231 mic ophone calib a o . Since some o he mic ophones a e posi ioned close o he ailway, some in luence o po- en ial ai - low gene a ed by he ain passage will ine i ably be included in he egis e ed esponses. Howe e , he egis e ed acous ic signals a e s ill ele an o be e unde s and he acous ic esponses a posi ions close o he ailway, since sound p essu e le els a such posi ions g ea ly helps o de ine e ec i e mi iga ion measu es o ackle he exposu e o pedes ians and sensible ecei e s. Figu e 3. Expe imen al se up con igu a ion. Appl. Sci. 2022,12, 2960 5 o 18 (a) Appl. Sci. 2022,1, 0 5 o 19 (a) (b) Figu e 4. Pho og aphs o he in si u expe imen al cha ac e isa ion. ( a ) Pho og aph o he mic ophones on si e. (b) Pho og aph o he measu emen se up in he p esence o he ehicle. The sound p essu e le els (SPL) collec ed in a ballas ack con ex in each o he ou a ailable mic ophones a e shown below, in Figu e 5. F om he expe imen al cha ac e isa ion i was possible o collec da a om nume ous passages wi h di e en unning speeds. In o de o summa ise he da a collec ed, he noise le els co esponding o he wo eco ded speed ( espec i ely, 84 km/h and 78 km/h) eco ded a e p esen ed. The da a a e p esen ed in one- hi d oc a e bands and i is in ended o highligh om among he a ious ecei e s he mos signi ican spec al con en ha will se e as a basis o he nume ical simula ions explained in he p e ious sec ions. 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 1 (M1) V=84km/h V=72km/h (a) 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 2 (M2) V=84km/h V=72km/h (b) 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 3 (M3) V=84km/h V=72km/h (c) 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 4 (M4) V=84km/h V=72km/h (d) Figu e 5. Reco ds o measu ed sound p essu e le els; in blue a ehicle ope a ing a 84 km/h; in yellow a ehicle ope a ing a 72 km/h. ( a ) Fi s mic ophone; ( b ) Second mic ophone; ( c ) Thi d mic ophone; (d) Fou h mic ophone. Sound p essu e le els (SPL), p esen ed in Figu e 5a e il e ed o ake in o accoun he esponse o he human ea , and hus a e p esen ed in dB(A). By analysing he one- hi d oc a e bands p esen ed, i is concluded ha he mos p e alen equency con en esponsible o he highes noise le els is be ween 200 Hz and 4000 Hz, i.e. he equency in e al be ween he wo discon inuous black lines in each o he hi d oc a e bands. This in o ma ion has been he basis o he nume ical modelling p esen ed la e in his pape , (b) Figu e 4. Pho og aphs o he in si u expe imen al cha ac e isa ion. ( a ) Pho og aph o he mic ophones on si e. (b) Pho og aph o he measu emen se up in he p esence o he ehicle. The sound p essu e le els (SPL) collec ed in a ballas ack con ex in each o he ou a ailable mic ophones a e shown below, in Figu e 5. F om he expe imen al cha ac e isa ion i was possible o collec da a om nume ous passages wi h di e en unning speeds. In o de o summa ise he da a collec ed, he noise le els co esponding o he wo eco ded speed ( espec i ely, 84 km/h and 78 km/h) eco ded a e p esen ed. The da a a e p esen ed in one- hi d oc a e bands and i is in ended o highligh om among he a ious ecei e s he mos signi ican spec al con en ha will se e as a basis o he nume ical simula ions explained in he p e ious sec ions. 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 1 (M1) V=84km/h V=72km/h (a) 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 2 (M2) V=84km/h V=72km/h (b) 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 3 (M3) V=84km/h V=72km/h (c) 20 40 60 100 200 400 1k 2k 4k 6k 10k 20k F equency [Hz] 0 10 20 30 40 50 60 70 80 90 100 Sound P essu e Le el [dBA] Mic ophone 4 (M4) V=84km/h V=72km/h (d) Figu e 5. Reco ds o measu ed sound p essu e le els; in blue a ehicle ope a ing a 84 km/h; in yellow a ehicle ope a ing a 72 km/h. ( a ) Fi s mic ophone; ( b ) Second mic ophone; ( c ) Thi d mic ophone; (d) Fou h mic ophone. Sound p essu e le els (SPL), p esen ed in Figu e 5a e il e ed o ake in o accoun he esponse o he human ea , and hus a e p esen ed in dB(A). By analysing he one- hi d oc a e bands p esen ed, i is concluded ha he mos p e alen equency con en esponsible o he highes noise le els is be ween 200 Hz and 4000 Hz, i.e., he equency in e al be ween he wo discon inuous black lines in each o he hi d oc a e bands. This in o ma ion has been he basis o he nume ical modelling p esen ed la e in his pape , Appl. Sci. 2022,12, 2960 6 o 18 allowing he de ini ion o he equency ange and con en ha needs o be mi iga ed by he noise ba ie . 3. Expe imen al Cha ac e isa ion o Po ous Conc e e In he po ous conc e e ma e ial, g anules a e usually dis ibu ed di e en ly om he wha is obse ed in ib ous ma e ials by ollowing a log-no mal po e dis ibu ion, esul ing in smalle po osi y and highe o uosi y. The abso p ion coe icien o hese ma e ials depends on he size o he po es, he po osi y, he o uosi y and he hickness o he ma e ial sample. Six samples o po ous conc e e we e p oduced using expanded clay agg ega es, wi h g ain size o 0–2 mm. All samples we e p epa ed wi h 10.1 cm o diame e and hickness o 4, 6 and 8 cm, being hese p ocedu e p e iously p esen ed in [ 23 ]. The sample p opo ions in weigh (kg) a e p esen ed in Table 1. Table 1. Ma e ials p opo ions in weigh (kg) o he p oduced samples. G ain Size (mm) Agg ega e (%) Cemen (%) Wa e (%) 0–2 43.96 37.36 18.68 Se e al app oaches can be used o cha ac e ise acous ic abso bing ma e ials, such as hose desc ibed o example in Ciabu o e al. [ 28 ], A enas e al. [ 29 ] o del Rey e al. [ 30 ]. He e, an expe imen al expe imen al p ocedu e based on he use o an impedance ube was used o cha ac e ise he no mal incidence acous ic p ope ies o he po ous conc e e samples. As desc ibed in ISO 10534-2 [ 31 ], hese p ope ies can be ob ained om he ans e unc ion be ween wo mic ophones. To ob ain he in insic acous ic p ope ies o he po ous conc e e samples, he Two-Ca i y Me hod p oposed by U suno e al. [32] was used. The impedance ube used has a ci cula c oss-sec ion o 10.1 cm diame e , he cu -o equency being app oxima ely 1600 Hz o he chosen mic ophone spacing. A whi e noise signal was used o exci e he speake om he analyse , OR 34 Compac Analyze , he sound p essu e was measu ed using wo mic ophones B&K Type 4188 1/2 00 , posi ioned a 16 cm and 10 cm om he sample su ace, and he p essu e da a we e pos -p ocessed in Ma lab, o ob ain bo h he su ace impedance and he sound abso p ion. A schema ic ep esen a ion o he expe imen al se up is p esen ed in Figu e 6, whe e he e m d1 is he sample hickness, and D is he ai ca i y hickness. Figu e 6. Schema ical ep esen a ion o he expe imen al wo-ca i y me hod ( e ie ed om [23]). The wo-ca i y me hod is based on wo measu emen s o he same sample h ough he ISO 10534-2 p ocedu e. Each measu emen uses a di e en ai ca i y dep h, D, be ween he sample and he igid e mina ion. The complex cha ac e is ic impedance, ˜ Zc , and he complex wa e numbe , ˜ kc , can be de e mined, espec i ely, by he ollowing equa ions, ˜ Zc=s˜ Zs1˜ Zs2Z1−Z0 1−Z1Z0 1˜ Zs1˜ Zs2 Z1−Z0 1−˜ Zs1˜ Zs2, (1) Appl. Sci. 2022,12, 2960 7 o 18 ˜ kc=j 2d1 ln˜ Zs1+˜ Zc ˜ Zs1−˜ Zc ˜ Zs2+˜ Zc, (2) whe e d1 is he sample hickness, ˜ Zs1 is he complex su ace impedance measu ed wi h he i s ai ca i y dep h D, and ˜ Zs2 is he complex su ace impedance measu ed wi h he second ai ca i y dep h D 0 . Z1 and Z0 1 deno e he acous ic impedance o each ai ca i y, Z1=−jρ0c0co (k0D), (3) Z0 1=−jρ0c0co k0D0. (4) The measu emen s we e pe o med o a igid e mina ion and an ai ca i y dep h D = 2 cm. This op ion p ese es he me hod’s alidi y and allows minimising he numbe o measu emen s o each sample o de e mine bo h i s sound abso p ion coe icien and i s in insic acous ic p ope ies. Figu e 7shows he po ous conc e e samples and sound abso p ion cu es be ween samples wi h di e en hicknesses. Each cu e co esponds o he a e age be ween he wo samples o same hickness, espec i ely, 4, 6 and 8 cm. I was obse ed ha he inc ease in he hickness p oduces a shi in he sound abso p ion coe icien cu e owa ds low equencies. (a) (b) Figu e 7. Sound abso p ion beha iou o po ous conc e e. ( a ) Po ous conc e e buil samples. ( b ) A e age o he sound abso p ion coe icien o h ee di e en hicknesses: 4, 6, and 8 cm. ( e ie ed om [23]). To p edic he acous ic beha iou o po ous conc e e wi h di e en hicknesses and o ep esen hese ma e ials as he luid-equi alen heo y, he Ho oshenko and Swi model was used [33]. This model was de i ed assuming igid ame g anula media wi h a log-no mal po e size dis ibu ion o p edic he he cha ac e is ic impedance, ˜ Zc , and he wa e numbe , ˜ kc , o po ous conc e e samples. I conside s ou mac oscopic pa ame e s o de e mine he acous ic beha iou : ai low esis i i y, σ , open po osi y, φ , o uosi y, τ , and he s anda d de ia ion o he po e size, σp. The in e se echnique was pe o med using a gene ic algo i hm in which he objec i e unc ion was based on he quad a ic sum o e o s be ween he analy ical and expe imen al da a, along a equency ange wi h n disc e e equency alues, OF(ω) = n ∑ i=1αana −αexp, (5) whe e αana is he abso p ion coe icien ob ained om he Ho oshenko and Swi model [ 33 ], and αexp is he expe imen al abso p ion coe icien . These ou mac oscopic pa ame e s we e p e iously ob ained in [ 23 ], and a e p esen ed in Table 2. The open Appl. Sci. 2022,12, 2960 8 o 18 po osi y was he only mac oscopic pa ame e expe imen ally de e mined, using he wa e sa u a ion me hod. Table 2. Mac ospic pa ame e s ob ained o he po ous conc e e s udied samples. Ai low Resis i i y σ [Ns/m4]Open Po osi y φ[-] To uosi y α∞[-] S anda d De ia ion o he Po e Size σp [-] 3896.06 0.46 1.89 0.25 Figu e 8shows a compa ison be ween he complex p ope ies using he p esen ed mac oscopic pa ame e s and hose expe imen ally ob ained h ough he wo-ca i y me hod o a sample wi h 4 cm. As obse ed in [ 34 ], an excellen ag eemen can be obse ed be ween he expe imen al da a and he semi-phenomenological p edic ion, allowing us o ep esen and p edic he po ous conc e e beha iou o di e en samples hicknesses and geome ies. 200 400 600 800 1k 1.2k 1.4k 1.6k F equency [Hz] - 1000 - 500 0 500 1000 1500 2000 Cha ac e is ic impedance [Pa.s/m] Real Two-Ca i y Me hod Imag. Two-Ca i y Me hod Real Ho oshenko -Swi Model Imag. Ho oshenko -Swi Model (a) 200 400 600 800 1k 1.2k 1.4k 1.6k F equency [Hz] - 20 0 20 40 60 80 Wa enumbe [ ad/m] Real Two-Ca i y Me hod Imag. Two-Ca i y Me hod Real Ho oshenko -Swi Model Imag. Ho oshenko -Swi Model (b) Figu e 8. Compa ison be ween he expe imen al cha ac e isa ion and he semi-phenomenological ep esen a ion n. (a) Cha ac e is ic impedance, ˜ Zc. (b) Wa e numbe , ˜ kc( e ie ed om [34]). 4. Nume ical Modelling The Bounda y Elemen Me hod, BEM, was used o model he acous ic p oblem since i allows analysing complex geome ies wi hou he need o desc ibe he whole p opaga ion medium, and allows us o sol e p oblems wi h bo h in ini e o limi ed domains [6]. In he equency domain, he p oblem is go e ned by he Helmhol z equa ion, ∇2p+k2p=δ( 1− 0). (6) whe e pis he acous ic p essu e and k is he wa e numbe . The de elopmen o Equa ion (6) yields Equa ion (7), which allows he acous ic p ob- lem o be sol ed by in eg a ion along he de ined bounda ies. Thus, sol ing Equa ion (7) can be de ined as app oxima ing he solu ions o each bounda y elemen j. N ∑ j=1 (x,~ n)ZΓiρωG(x,x0)dΓj+ N ∑ j=1 p(x)ZΓH(x,x0,~ n)dΓj+cpp(x0)=pinc x0,x (7) Usually, he ma ix o mula ion is used as he p e e ed means o ca y ou he Bound- a y Elemen Me hod [35,36], Cp−Hp=iρ0ωG +pinc. (8) Appl. Sci. 2022,12, 2960 9 o 18 whe e pand a e he acous ic quan i ies o be calcula ed— he p essu e and eloci y o pa icles acco ding o he su ace—and pinc is he acous ic p essu e in he ee ield due o a sou ce loca ed on he domain. The G and H ma ices a e ully popula ed ma ices. Finally, Cis a diagonal a ay whose alues depend on he colloca ion poin . I is common o add he ma ix Cand H, w i ing he p e ious equa ion in i s mos simpli ied o m, Hp=iρ0ωG +pinc. (9) The o mula ion p esen ed up o his poin only allows he s udy o he in e ac- ion o he bounda ies wi h a single ex e nal medium, in his case, he acous ic medium. In o de o ep esen he po ous ma e ials ha a e o be placed on he ba ie and ha will be s udied in his documen , i is necessa y o ex end he me hod o include he simula ion o po ous ma e ials as luid-equi alen s. In o he wo ds, i is necessa y o simula e mo e han one p opaga ion medium, wi h di e en p ope ies. The e o e, i is necessa y o de ine each o he media and ensu e ha in he in e aces be ween hem he e is coupling be ween he p essu es and no mal eloci y. The sys ema isa ion o his p oblem in ol es he de ini ion o he equa ions p esen ed in Equa ion (7) o each p opaga ion domain and he bounda ies alid o bo h he ex e nal, Ωex e io and in e nal domain, Ωi, as illus a ed in Figu e 9. Figu e 9. Rep esen a ion o he coupled in e io /ex e io p oblem. The coupling be ween domains is achie ed by ensu ing equilib ium and con inui y condi ions a he sha ed bounda ies o he domains [37]. pΩex =pΩin (10) 1 iωρΩex ∂pΩex ∂n=−1 iωρΩn ∂pΩin ∂n(11) The calcula ion p ocess in ol es sol ing a sys em o equa ions aking in o accoun he equa ions de ined o he wo mediums unde conside a ion (Equa ion (7)). The sys em o equa ions can be exp essed as (iωρΩex GΩex {˜ }+HΩex {ˆ p}={¯ pinc}, o ai −iω˜ ρΩjGΩj{¯ }+HΩj{¯ p}=0, o po ous ma e ial (12) Once he acous ic a iables a he de ined bounda ies a e known, he acous ic p essu e a he ex e nal ecei e s is equal o he sum o he inciden acous ic p essu e and he acous- ic p essu e esul ing om he in e ac ion o he bounda ies wi h he acous ic medium, as shown in Equa ion (13). pT=pinc +pS(13) Appl. Sci. 2022,12, 2960 16 o 18 Figu e 20. Inse ion loss maps o he cu ed noise ba ie wi h abso p i e laye o equencies 315 Hz, 400 Hz, 500 Hz, 630 Hz, 800 Hz and 1000 Hz ( a – ), wi h he p esence o he ecei e s (black do s) used o calcula e mean IL (Figu e 18). Figu e 21. Inse ion loss maps o he cu ed noise ba ie wi h abso p i e laye o equencies 1250 Hz, 1600 Hz, 2000 Hz, 2500 Hz, 3150 Hz and 4000 Hz ( a – ), wi h he p esence o he ecei e s (black do s) used o calcula e mean IL (Figu e 18). 7. Conclusions This pape p esen s he de elopmen o a low-heigh acous ic ba ie o be used close o he noise sou ce in a ailway en i onmen . The de elopmen o he solu ion is composed by wo dis inc phases, namely he op imisa ion o he ba ie geome y and he in eg a- ion o a po ous ma e ial in o de o inc ease he acous ic pe o mance o he solu ion. Taking ad an age o sound p essu e le el eco ds acqui ed in he ailway en i onmen in he me opoli an a ea o Po o, i was possible o de ine he mos impo an equency con en and hus design a solu ion whose pe o mance was supe io in ha equency ange. The nume ical modelling and s udy o he a ious solu ions we e ca ied ou by applying a BEM o mula ion wi h mul iple egions, simula ing he po ous ma e ial as an equi alen luid and hus inco po a ing i s acous ic abso p ion p ope ies. The pa ame ic s udy p esen s he me hodology o sizing he cu ed ba ie . Th ough he simula ion o a sound wa e, he inne ace o he ba ie was cons uc ed so ha i coincides wi h he shape o he inciden wa e on coming om he sou ce. Thus, he e lec ion no mal o he p opaga ion di ec ion is a ou ed and, as such, mo e ene gy is sen in he di ec ion o he noise sou ce and he ailway. In his way, an in eg a ed solu ion was buil aking Appl. Sci. 2022,12, 2960 17 o 18 ad an age o he acous ic abso p ion capaci y o he ack o abso b he ene gy sen back. In a complemen a y manne , a po ous conc e e laye was added, which on he one hand has a good acous ic abso p ion capaci y and on he o he hand gua an ees he du abili y equi ed o solu ions used ou doo s. The main pu pose o he po ous ma e ial is o abso b pa o he ene gy a ising om he e lec ions be ween he ba ie and he ehicle, ensu ing ha he ene gy ha is no sen back o he ack can be sen in he di ec ion o he ex e nal ecei e s. The esul s p esen ed show he clea imp o emen achie ed by using po ous ma- e ial as a means o abso bing pa o he ene gy in de imen o pu ely e lec i e solu ions. The cu ed solu ion wi h po ous ma e ial p esen s an IL in he de ined ecei e s highe han 10 dB in all he calcula ed equency ange; o some equencies he IL alue is e en highe han 15 dB, wi h he maximum egis e ed in he equency 3150 Hz whe e he IL alue is highe han 25 dB. In his way, he p esen ed solu ion appea s o be an use ul elemen o he educ ion in ain-induced noise, gua an eeing an e ec i e mi iga ion. In addi ion, due o i s low-heigh , his solu ion does no ep esen a isual obs acle, as is usual o noise ba ie s, bu i s ill e ec i ely educes noise le els a he ecei e s o in e es . Au ho Con ibu ions: Concep ualisa ion, J.L., M.P., P.A.C. and L.G.; me hodology, J.L., M.P., P.A.C. and L.G.; so wa e, J.L., M.P. and L.G.; alida ion, J.L., M.P., P.A.C. and L.G.; o mal analysis, J.L., M.P., P.A.C. and L.G.; in es iga ion, J.L. and M.P.; esou ces, J.L., M.P., P.A.C. and L.G.; da a cu a ion, J.L. and M.P.; w i ing—o iginal d a p epa a ion, J.L. and M.P.; w i ing— e iew and edi ing, P.A.C. and L.G.; isualisa ion, J.L., M.P., P.A.C. and L.G.; supe ision, P.A.C. and L.G.; p ojec adminis a ion, P.A.C. and L.G.; unding acquisi ion, J.L., P.A.C. and L.G. All au ho s ha e ead and ag eed o he published e sion o he manusc ip . Funding: This esea ch was unded by Base Funding—UIDB/04708/2020 and P og amma ic Funding—UIDP/04708/2020 o he CONSTRUCT—Ins i u o de I&D em Es u u as e Cons uções— unded by na ional unds h ough he FCT/MCTES (PIDDAC); Base Funding—UIDB/04029/2020— o ISISE (Ins i u e o Sus ainabili y and Inno a ion in S uc u al Enginee ing) unded by na ional unds h ough he FCT/MCTES (PIDDAC); P ojec POCI-01-0247-FEDER-033990 unded by FEDER unds h ough COMPETE2020—P og ama Ope acional Compe i i idade e In e nacionalização (POCI); Na ional unds (PIDDAC) h ough FCT/MCTES; Indi idual G an : SFRH/BD/148367/2019. Con lic s o In e es : The au ho s decla e no con lic o in e es . Re e ences 1. EEA (Eu opean En i onmen Agency). En i onmen al Noise in Eu ope—2020; Technical Repo ; EEA (Eu opean En i onmen Agency): Copenhagen, Denma k, 2020; ISBN 9789294802057. 2. Blanes, N.; Ma in, A.; Ramos, U.M.J. 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