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Re se ar c h and applic ations of nanomate r ials in Cultur al He r itage
SIL VE ST RO ANT ONIO RUF F OL O
UNI VE RSIT À DE L L A CAL ABRI A
Re se ar c h and applic ations of nanomate r ials in Cultur al - - PDF document
01/02/2017 Re se ar c h and applic ations of nanomate r ials in Cultur al He r itage SIL VE ST RO ANT ONIO RUF F OL O UNI VE RSIT DE L L A CAL ABRI A Unive rsity o f Ca la b ria -Co se nza - 1 01/02/2017 Unive rsity
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SIL VE ST RO ANT ONIO RUF F OL O
UNI VE RSIT À DE L L A CAL ABRI A
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14 De pa rtme nts 34500 Stude nts 836 Pro fe sso rs & Re se a rc he rs 200 he c ta re s o f surfa c e 3000 sle e ping a c c o mmo da tio ns Ca nte e ns: 3500 me a ls e a c h da y 2 the a tre s
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Gino M. Crisc i (F
ull pro fe sso r)
Do na te lla Ba rc a (Asso c ia te pro fe sso r) Ma uro F
. L a Russa (Re se a rc he r)
Do me nic o Mirie llo (Re se a rc he r) Silve stro A. Ruffo lo (Re se a rc h fe llo w) Mic he la Ric c a (Re se a rc h fe llo w) Na talia Ro ve lla (Co ntra c to r) Ra ffa e lla De L
uc a (Co ntra c to r)
Va le ria Co mite (Co ntra c to r)
T
(sto ne ma te ria ls)
Arc he o me tric Ana lysis Arc he o me tric Ana lysis
K no wle dg e
Pro ve na nc e a na lysis
Sc ie ntific Suppo rt to Re sto ra tio n a nd Co nse rva tio n Sc ie ntific Suppo rt to Re sto ra tio n a nd Co nse rva tio n
De g ra da tio n Co nse rva tio n stra te g ie s
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Wha t is na no te c hno lo g y Why we sho uld a pply na no te c hno lo g y
to re sto ra tio n o f Cultura l He rita g e
Sta te o f a rt o f re se a rc h Co nso lida tio n with na no pa rtic le s Pro te c tio n with na no pa rtic le s
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T he study o f the c o ntro lling o f ma tte r
Ge ne ra lly na no te c hno lo g y de a ls with struc ture s size d b e twe e n 1 to 100 na no me tre s in a t le a st o ne dime nsio n, a nd invo lve s de ve lo ping o r mo difying ma te ria ls o r de vic e s within tha t size .
So urc e : http:/ / sinte fi.b lo g spo t.it/ 2013/ 05/ na no fib ra .html
A Huma n Ha ir is a b o ut 100 µm wide
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Nanote c hnology
Infor ma tion T e c hnolog y Me c ha nic a l E ngine e r ing Biote c hnology T r a nspor ta tion National Se c ur ity & De fe nse F
Agr ic ultur e Me dic ine / He a lth Ae r
E ne r g y & E nvir
Adva nc e Ma te r ia ls & T e xtile s R e stor a tion of Cultur a l He r ita g e
Applic ations of nanote c hnology in Cultur al He r itage
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Ca (OH)2 + CO 2 CaCO 3 + H2O
Solubility of Ca (OH)2 = 1.7 g/ l (0.17% ) A satur e d solution of Ca (OH)2 is c alle d lime wate r
If I add mor e lime I will obtain a milky suspe nsion c alle d milk of lime T he main pr
e late d the dime nsion of the par tic le s (sc ar c e pe ne tr ation)
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Ba g lio ni & Gio rg i 2006
SiO 2 SiO 2
30 nm Unb o nb e d pa rtic le s
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SiO 2 SiO 2
30 nm b o nb e d pa rtic le s
Str e nghts
e ss se nsitive to mic ro c lima tic c o nditio ns
Str e nghts
e ss se nsitive to mic ro c lima tic c o nditio ns
We akne sse s
We akne sse s
Oppor tunitie s
mo rta rs
Oppor tunitie s
mo rta rs
T hr e ats
lo c c ula tio n with sa lts
issue s T hr e ats
lo c c ula tio n with sa lts
issue s
SWOT SWOT
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Cappadoc ia
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20000 40000 60000 80000 100000 120000 140000 160000 180000 200000
2016 2015 2014 2013 2012 2011 2010 2009 2008 2007 2006 2005 2004 2003 2002 2001 2000 1999 1998 1997 1996
Pape r s
Nanopar tic le s Gr aphe ne Cultur al He r itage T itanium dioxide
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10000 20000 30000 40000 50000 60000 70000 80000
2016 2015 2014 2013 2012 2011 2010 2009 2008 2007 2006 2005 2004 2003 2002 2001 2000 1999 1998 1997 1996
Pape r s
Nanopar tic le s Gr aphe ne Cultur al He r itage T itanium dioxide
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50 100 150 200 250 300 350
2016 2015 2014 2013 2012 2011 2010 2009 2008 2007 2006 2005 2004 2003 2002 2001 2000 1999 1998 1997 1996
Pape r s
Cultur al He r itage + Nanopar tic le s
T
Ra tio (Na no te c hno lo g y + Cultura l He rita g e )/ Cultura l He rita g e : 1.5%
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Stone de gr adation
Biologic al fac tor s Che mic al fac tor s Physic a l fac tor s
SAL T CRYST AL L ISAT ION
Whe n a salt-ric h so lutio n pe ne trate s into the po re struc ture , in spe c ific supe rsaturating and the rmo dynamic c o nditio ns, the salt c rystallizatio n take s plac e and nuc le atio n and gro wth o f salt c rystals within the po re spac e s c an induc e alte ratio n and de gradatio n o f the sto ne
SAL
T SOL UT ION
POROUS
MAT E RIAL
PRE
CIPIT AT ION
G ROWT
H OF SAL T CRYST AL S WIT HIN T HE PORE
WE
AT HE RING
Efflo r e sc e nc e Cr ac ks (Sub-e fflo r e sc e nc e )
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T he c rystallizatio n pre ssure o f salt c rystals, gro wing in c o nfine d po re s, is fo und to be the main c ause fo r damage T he pre ssure e xe rte d by salt c rystals o n the c apillary wall, is dire c tly pro po rtio nal to salt c o nc e ntratio n and c rystal size , and inve rse ly pro po rtio nal to the radius o f the po re
Afte r c rystalgro wth T he po re struc ture is c o mpro mise d due to pre ssure e xe rte d by the c rystal
Ne w Mic ro c rac ks
SAL T CRYST AL L ISAT ION
Salt crystallisation process
The crystal growth generates pressure
Crystal
Due to the pressures, the pore increases its size
E fflor e sc e nc e Cr ac ks
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Salt c r ystallization + wind = Alve olization
Alve olization?
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Ne w insig hts o n the CONS OL I DAT I ON
c a se study o f Mo dic a Sto ne
Ruffo lo e t al 2015, Bulle tin o f E ngine e ring Ge o lo gy and the E nviro nme nt
Pe tro g ra phic o b se rva tio ns (Be lfio re e t a l. 2010) re ve a le d a g ra in-suppo rte d te xture with a b o ut 30% o f mic ritic ma trix. Allo c he mic a l c o mpo ne nts, with pe rc e nta g e s b e twe e n 40 a nd 45%, c o nsist o f se ve ra l b io c la sts.
T he po ro sity (a b o ut 27%) is ma inly inte rg ra nula r. Ac c o rding to Dunha m (1962), the Mo dic a sto ne c a n b e c la ssifie d a s a pa c ksto ne , a c c o rding F
b io mic rite .
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Ruffo lo e t al 2015, Bulle tin o f E ngine e ring Ge o lo gy and the E nviro nme nt
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Ruffolo e t al.
Sub mitte d to I nte rna tio na l Bio de te rio ra tio n & Bio de g ra da tio n
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Biologic al de gr adation of stone sur fac e s Use of bioc ide s in r e stor ation
fac e s
I
n the e a rly sta g e s o f c le a ning o f a n a re a a ffe c te d b y b io lo g ic a l de g ra da tio n, a funda me nta l o pe ra tio n is re pre se nte d b y the re mo va l o f b io lo g ic a l pa tina s
T
he re mo va l o f b io lo g ic a l pa tina s re q uire s the use o f b io c ide s (o rg a nic c o mpo unds in a q ue o us o r o rg a nic so lve nt)
T
he re mo va l o f b io lo g ic a l pa tina s do e s no t e nsure a n inhib iting e ffe c t o ve r time
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Be fo re During Afte r
A pro duc t tha t c a n a ssure a n inhib itio n e ffe c t c a n pro duc e b e ne fits:
E
c o no mic : le ss c le a ning inte rve ntio ns
pa tina
E
nviro nme nta l: linke d to re duc e d use o f b io c ide s a nd so lve nts
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Color ing age nt E 171 T itanium dioxide
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UV light < 390 nm
Se lf c le aning e ffe c t and bioc idal e ffe c t
s on titania sur fac e
01/02/2017 26 1 g T iO 2 2.3 c m 2 0.0023 m 2 0.23 c m
Par tic le size 0.01 c m
141 c m 2 0.0141 m 2
01/02/2017 27 1g T iO 2 Par tic le size 25 nm:
300 m 2
40 g T iO 2 12000 m 2
By doping the T iO 2 it is possible to e nhanc e the e ffic ie nc y In lite r atur e ma ny doping me tals have be e n use d for this pur pose
M- Dope d T iO 2
Za le ska , 2008
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Ag-dope d titania e nhanc e s the photoc atalitic e ffe c t F r e e silve r c an ac t itse lf as antimic r
T he c olour be c ome dar ke r
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E xpe r ime ntal
Synthe sis and physic al/ c he mic al c har ac te r ization of T iO 2, and dope d T iO 2 E ffic ie nc y asse ssme nt In vitr
ime ntation Me thyle ne Blue de gr adation Choic e of the most suitable binde r
In Situ applic ation
ID mate r ial
Pr e c ur sor Ac id (1 ml)
T
volume (ml) Re ac tion r ate
1 T iO 2 T BT HCl 0,01M 25 F a st 2 T iO 2 T PT HCl 0,01M 25 F a st 3 5% Ag -T iO 2 T BT HCl 0,01M 25 F a st 4 1% Ag -T iO 2 T BT HCl 0,01M 25 F a st 5 5% Sr-T iO 2 T BT HCl 0,01M 25 F a st 6 1% Sr-T iO 2 T BT HCl 0,01M 25 F a st 7 T iO 2 T PT HCl 1M 25 Slo w 8 T iO 2 T PT HCl 1M 25 Slo w 9 T iO 2 T PT Ac e tic Ac id 1M 25 F a st 10 T iO 2 T PT Ac e tic Ac id 1M 25 F a st 11 T iO 2 T PT Ac e tic Ac id Gla c ia l 3 Ve ry Slo w 12 1% Ag -T iO 2 T PT Ac e tic Ac id Gla c ia l 3 Ve ry Slo w
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With UV Radiation Without UV r adiation
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0,170 0,370 0,570 0,770 0,970 1,170 1,370 1,570
1 2 3 4 5 6 OD
T ime [hour s] T iO 2
0,5 mg/ ml 0,25 mg/ ml 0,1 mg/ ml 0,05 mg/ ml 0,01 mg/ ml c ontrol wate r
Growth inhibition assay of E sc he ric hia c oli and mic robial viability te st
0,170 0,370 0,570 0,770 0,970 1,170 1,370 1,570
1 2 3 4 5 6 OD
T ime [hours]
Ag- T iO 2 1%
0,5 mg/ ml 0,25 mg/ ml 0,1 mg/ ml 0,05 mg/ ml 0,01 mg/ ml c ontrol wate r
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SE M o b se rva tio n o f b a c te ria l a ) witho ut c o nta c t with na no b io c ide s (c o ntro l) a nd b ) a fte r 30 min o f c o nta c t with Ag T
e mb e dde d into the Ag do pe d tita nia pa rtic le s. Arro ws indic a te the b a c te ria
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Binde r nPs Stone
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I
no rg a nic
Minima l inte rfe re nc e with the
e ffic a c y o f tita nia 3 binde r s have be e n te ste d
Ammo nium pho spha te Ammo nium o xa la te Na no Silic a
nanoSilic a Phosphate Oxalate
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na no Silic a ha s sho w the b e st b e ha vio r, pro b a b ly due to the hig he r pH whic h e nha nc e s the pho to c a ta lytic e ffe c t
UNDE RST ANDI NG T HE BE HAVI OR OF T HE COAT I NGS I N RE AL SI T UAT I ONS
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F
r e vi Roman the r mae Re ggio Calabr ia E r c olano, Villa de i Papir i
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Sampling be for e c le aning
Sa mple s ha ve b e e n ta ke n b y using a no n-de struc tive sa mpling me tho d o f a dhe sive ta pe strips (F ung ita pe Did, Mila n, I ta ly) a s de sc rib e d b y Urzì a nd De L e o , 2001)
Cle aning phase
T he surfa c e s wa s first tre a te d with a so lutio n o f Bio tin R (CT S, I ta ly). T he a pplic a tio n ha s b e e n c a rrie d o ut b y b rush. T he tre a tme nt ha s b e e n re pe a te d thre e time s (e ve ry 15 da ys),a nd the n the surfa c e s ha ve b e e n rinse d with de io nise d wa te r.
Sampling afte r c le aning
Sa mple s ha ve b e e n c o lle c te d to c he c k the re sidua l b io c o lo niza tio n
T itania tr e atme nt
Dispe rsio ns o f na no silic a a nd tita nia ha ve b e e n a pplie d o n sto ne surfa c e s b y b rush a t a mo unt o f a b o ut 400 ml/ m2
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Monitoring after TiO2 treatment
9 samples. Check the bio inhibition feature
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Ba c te ria l, F ung i a nd Pho to tro phs I de ntific a tio n a nd q ua ntific a tio n
Mic ro sc o pic o b se rva tio ns SE
M a na lysis
Cultura l a na lyse s I
T S-PCR fo r b a c te ria
16SrDNA pa rtia l se q ue nc ing fo r Ba c te ria DNA e xtra c tio n a nd PCR a mplific a tio n fo r fung i
Table 2. Amount of chemoorganotrophic microorganisms determined as cfu/g or as different degree
Sample Bacteria (cfu/g) Fungi (cfu/g) Phototrophs (Presence/absence) ERB1 3.2·105 2.0·104 ++++++ ERB2 6.5·104 4.4·106 ++++++ ERB3 7.2,·105
++ ERB4 2.9·106 3.0·106
8.0·107
++++ ERB6 1.1·108
ERB7 4.4·107 1.0·104
2.1·107
++++ ++++++ (very abundant growth); ++++ (abundant growth), ++ (discrete growth), + (scarce growth).
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F re q ue nc y o f fung i iso la te d fro m the diffe re nt E RB sa mple s prio r a ny tre a tme nt a nd the ir ta xo no mic a ttrib utio n. F re q ue nc ie s o f b a c te ria l iso la te s fro m sa mple s E RB ta ke n prio r a ny tre a tme nt a nd the ir ta xo no mic a ttrib utio n
. Summary of cultural analysis carried out after 1 months of biocide treatments Sample Bacteria cfu/cm2 Fungi cfu/cm2 Phototrophs Presence/absence ERBD1 145 ERBD2 75 ERBD3 65 6 + ERBD4 15 ERBD5 50
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Bacteria, fungi and phototrophs growing in BRII, DRBC e BG11 respectively after streaking on the surface 1 cm2 of adhesive tape. Samples are divided on the basis of the treatment as shown in Plate Ic. Samples Treatment* Bacteria Fungi Algae ERBN1 B5%+Ag-TiO2
++ ERBN2
++ + +/- ERBN8 + +
B ++ + +++ ERBN9 + +
ERBN5 B10%+TiO2 ++ +
ERBN6 B5%+TiO2 + +
TiO2 +/- + + * = Binder; - = no growth; +/-= scarce growth; +=occasional growth; ++= discrete growth; +++= abundant growth.
I n Ma y 2016 the
na tio na le de sé c urité sa nita ire de l'a lime nta tio n, de l'e nviro nne me nt e t du tra va il – ha s sub mitte d a CL H pro po sa l to E CHA to c la ssify tita nium dio xide a s 1B with ha za rd sta te me nt H350i (Ma y c a use c a nc e r b y inha la tio n)
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ANNE X 2 - COMME NT S AND RE SPONSE T O COMME NT S ON CL H PROPOSAL ON T IT ANIUM DIOXIDE
I
n o ur c a se study, Na no size d tita nium dio xide se e ms to ha ve a b io -inhibitio n e ffe c t (mitig a tio n)
A lo ng e r pe rio d o f mo nito ring is ne e de d to
unde rsta nd the lo ng -te rm b e ha vio r
T
he use o f the se ma te ria ls c o uld b e thre a te ne d b y its c la ssific a tio n b y E CHA
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POR Calabr ia F E SR pr
‘‘NANOPROT E CH’’ (NANO PROte c tion T e c hnology for Cultur al He r itage )