geochimica in sistemi naturali ed analisi

Presentazione sul tema: "geochimica in sistemi naturali ed analisi"— Transcript della presentazione:

1 geochimica in sistemi naturali ed analisi
Composti Organici: geochimica in sistemi naturali ed analisi

2 Types of analytical instruments
L’approccio classico prevede… Types of analytical instruments Personal Monitors Light weight monitors Can be conveniently carried or worn by a person Portable monitors Can be moved during sampling Stationary monitors Have to be operated from a fixed location Volatile Organic Compounds

3 Volatile Organic Compounds
Types of Sampling Active Sampling Contaminated air is directly drawn into a sensor or collector Provides a real time analysis of the sample Passive Sampling Air diffuses into the collector Longer period of time must be allowed for accurate results Volatile Organic Compounds

4 Volatile Organic Compounds
Sampling methods Principles of Sampling Collectors 1. Air displacement 2. Condensation 3. Gas washing or absorption 4. Adsorption Volatile Organic Compounds

5 Air Displacement Sampling Method
Evacuated flasks or plastic bags are used Samples are collected by opening the inlet to the contaminant-laden air Sample is subsequently analyzed using a suitable analytical method Volatile Organic Compounds

6 Condensation Sampling Method
Air is passed through a U-tube or a suitable container Sample is subsequently cooled to below the boiling point of the pollutant In most cases a liquid nitrogen cryogenic trap is used. Condensed liquid is eventually analyzed Volatile Organic Compounds

7 Gas washers/ Absorbers Sampling Method
Air containing the pollutants is bubbled through a liquid contained in an impinger An aliquot of the liquid is analyzed to determine the characteristics and concentrations of the pollutants Distilled water is commonly used for readily soluble gases A liquid medium that reacts with the pollutants should be avoided Volatile Organic Compounds

8 Gas washers/ Absorbers Sampling Method
This method is suitable only for a few specific pollutants such as Formaldehyde, Phenol and Ethylene Oxide Collection Efficiency can be increased by: Decreasing the flow rate Improving the distribution of gas phase in the liquid medium Increasing the residence time Using two or more collectors in series Volatile Organic Compounds

9 Adsorption Sampling Method
Used for measurement of emissions from materials. Emissions are measured either in an environmental chamber or through “head space” analysis Environmental Chamber Studies: Material is placed in a chamber Environmental parameters of the chamber (temperature, humidity, air exchange rates) are controlled precisely Air samples are collected in solid adsorbent tubes for later analysis with a gas chromatograph Volatile Organic Compounds

10 Adsorption Sampling Method
“Head-Space” analysis Small samples of the material are placed in a container Head space gases are collected and analyzed by a gas chromatograph Sampling time depends on the emission rate from the material Solid adsorption media are more popular Pollutants are allowed to adsorb for a predetermined period of time on a solid Most frequently used solid adsorbent is activated carbon and silica gel Volatile Organic Compounds

11 Adsorption Sampling Method
Factors for successful use of adsorbent cartridges Careful cleaning of the sorbent tube to remove background contamination Accurate determination of sampling rate Cleaning of cartridges Heat them at a high temperature under vacuum or by flowing inert gas through the cartridge Flow of inert gas should also continue during cooling Another method is to wash the cartridge with a solvent and dry it at a temp. of oC Volatile Organic Compounds

12 Analysis Methodologies
Colorimeters and Spectrophotometers Used to quantify a specific pollutant Utilize liquid reagents, chemically treated papers and glass indicating tubes Chromotropic acid method Most frequently used to determine the concentration of Formaldehyde Measured volume of sample air is drawn through distilled water into an absorber Collection efficiency greater than 95% is achieved by using two absorbers in series Volatile Organic Compounds

13 La miglior qualità dell’homo analyticus è la capacità d’adattamentto
Nella pratica…. La miglior qualità dell’homo analyticus è la capacità d’adattamentto

14 Campionamento da emissione puntuale di alta temperatura

15 Polle gorgoglianti

16 Fumarole

17 temperature fino a 700°C !!! condensatore pompa Linea pirex trappola
Campionamento di fumarole in trappole solide Tubo titanio Linea pirex temperature fino a 700°C !!!

18 ALOGENATI - ST Trappola Solida (ST): Carboxen B - Carboxen C – Carbapack 111 FUMAROLE ARIA Organici <C4 analizzati tramite GC-MS con TD Composti <C4 e maggiori analizzati tramite GC (FID e TCD)

19 Gas del suolo

20 Combinazione delle due tecniche
Aria (ST) Emissione puntuale (SPME+ ST) Emissione diffusa (SPME)

21 campionamento in aria Condizioni operative Basso flusso (250 cc/min)
elevati tempi prelievo (fino a 12 ore) no filtri stoccaggio immediato Possibilità flussaggio in laboratorio su capione prelevato in sacca (campionamento aereo)

22 campionamento gas disciolti
Condizioni operative No reagenti quantità ridotte (12-20 cc acqua) stoccaggio immediato No bolle aria Campionamento classico Testa ampolla pre-evacuata (legge Henry)

23 Le fasi analitiche Iniezione Separazione cromatografica
Frammentazione con pennello elettronico Rilevazione frammenti molecolari con quadrupolo

24 Protocollo analitico SPME Solid trap (ST) GC-MS thermal desorber
column headspace Purge & Trap

25 Gas massa

26 ANALYSIS OF INORGANIC COMPOUNDS AND CH4
Gaschromatography GC Ionic Chromatography IC (Montegrossi et al., 2001) ANALYSIS OF VOCs Gas Chromatography coupled with Gas-Mass GC-MS Thermo Trace GC Ultra with mass spectromrtry (MS) Thermo DSQ

27 iniezione

28 Desorbimento COV da trappole solide
Condizioni operative Gas carrier elio tempo desorbimento ST 20 min (230 °C) trappola focalizzatrice trifase (-5 °C) tempo desorbimento 2 min (250 °C) Iniezione in testa colonna tramite transfer line (termostata 230 °C)

29 Desorbimento COV da fibra SPME (Solid Phase Micro Extraction)
Tecnica SPME Desorbimento COV da fibra SPME (Solid Phase Micro Extraction)

30 Trasferimento campione da ampolla con fibra SPME
Iniezione da fibra SPME Spessore 30/50 μm; lunghezza 2 cm 3 fase DiVynilBenzene (DVB)-Carboxen-PoliDiMethylXyloxane (PDMX) su supporto (siringa) Esposizione alla fibra = 15 min. Desobimento in testa colonna: T= 230 °C, tempo 2 minuti

31 Analysis by mass spectrometry
Solid phase microextraction (SPME) Carboxen polymethylsiloxane Thermal desorbtion Selective capillary chromatography GS gas-pro column coupled with Quadrupole mass spectrometry

32 Estrazione fasi gassose da campioni liquidi
Tecnica Purge and Trap Estrazione fasi gassose da campioni liquidi

33 Tecnica Purge and Trap Estrazione fasi gassose da campioni liquidi
Condizioni operative Gas carrier elio tempo purge 20 min trappola focalizzatrice trifase tempo desorbimento 2 min Iniezione in testa colonna

34 Restituzione dato: Cromatogrammi Spettri di massa
Determinazione qualitativa Determinazione quantitativa

35 Analisi qualitativa: la separazione cromatografica

36 Analisi qualitativa: la colonne capillari

37 CROMATOGRAMMA SPETTRO MS TEMPO DI RITENZIONE AREA PICCO

38 Analisi qualitativa

39 Analisi quantitativa

40 Restituzione dato Concentrazioni per gas da emissioni puntali:
frazione molare (permil, ppm, ppb) Il dato di concentrazione di COV si raccorda/compara con quello delle altre specie gassose

41 Restituzione dato Concentrazioni gas disciolti:
frazioni molari e/o moli su litro Concentrazioni in aria: mol/m3 (rapporti stechiometrici) e/o g/m3 (limiti legge) Il dato di concentrazione di COV si rapporta ai limiti di legge

42