This page contains a Flash digital edition of a book.
DECONTAMINATION


Table 1. Testing panels (substrate samples). PCN*+++


PLF+++ Painted Concrete


circular 3.6 x 1.1 9.08 cm2


Lino Floor CARC+


Chemical Agent Resist. Coating


23.22 cm2 GYB+++ Gypsum board 15.21 cm2 BUR++ Butyl rubber


square 5 x 5 x 0.2 square 5 x 5 x 0.2 square 4 x 4 x 0.6 square 5 x 5 x 0.2 24.01 cm2


24.01 cm2 SDS+++ Raw sandstone


square 3 x 3 x 1.2 8.41 cm2


*Paint type: Flügger Denmark, Flutex 1 Plus acrylate paint for indoor surfaces - white)


Agents Resistance Coating (CAR) panels is very low compared to contamination density on Sandstone (SDS) substrate. Butyl Rubber (BUR) substrate shows comparable results to Gypsum Board (GYB). Low contamination density was found on Painted Concrete and Plastic Floor (PLF). On the basis of testing results,


LVD-X decontamination technology is effective in decontamination of selected indoor building surfaces that have been contaminated by vaporized CW agents. Materials resistant to the penetration of vaporized CW agents (CAR), as well as the adsorptive materials – such as PCN and GYB – are definitely decontaminated to below contact hazard threshold level using the


LVD-X Liquids


RED MIXING PIPELINE WHITE MIXING PIPELINE


AIR FLOW (m3.h-1)


1.8–2.0 1.8


+++ by Spiez Laboratories, CH, + by CRISTANINI, ++ by VOP CZ S.p.A. GB Agent


l Vaporized GB agent shows the highest affinity towards SDS l BUR significantly retains vaporized GB agent in the material structure


l GB agent decontamination performs extremely well, particularly for PCN, CAR, and GYB


l GD agent shows the highest affinity towards the SDS l BUR and PLF significantly retain vaporized GD in the material structure


GD Agent


l GD agent decontamination results in almost all tested substrates showed very good results, with PLF and BUR substrates showing the lowest decontamination efficacy


HD Agent


l HD agent showed a high affinity towards a wide scale of substrates (except CAR) l PLF, BUR and GYB significantly retain vaporized HD in the material structure


l HD agent residuals in all of the tested substrates are well decontaminated using LVD-X technology


standard LVD-X decontamination procedure. Decontamination of organic materials such as PLF and BUR, which are


Table 2. Main operating parameters for use of the LVD-X system.


LIQUID FLOW (dm3.h-1)


3.6 4.0


Table 3. CRISTANINI LVD-X Decontamination results chart.


INDOR BUILDING SURFACES


(PCN) Painted Concrete (PLF) Plastic floor


(CARC) Chem. agent Resistant Coating


(GYB) Gypsum Board Painted


(BUR) Butyl Rubber (SDS) Sandstone


GB


Initial Cont.


(mg.m-2) 63.88


126.01 29.89


282.68


Residual Cont.


(mg.m-2) 0.73


27.28 0.12


0.66


308.21 80.46 751.89


26.14


LVD-X Decon


efficiency (%)


98.86 78.35 99.57


99.77


73.90 96.52


Initial Cont.


(mg.m-2) 306.78


142.24 6.07


206.82


337.65 649.42


CW Agent GD


Residual Cont.


(mg.m-2) 0.26


54.21 0.13


6.38


66.24 16.95


LVD-X Decon


efficiency (%)


99.92 59.07 97.90


93.62


80.36 97.39


Initial Cont.


(mg.m-2) 262.03


91.99 0.76


272.80


180.76 181.72


AIR


PRESSURE (bar)


3.8–4.8 2.0–3.0


LIQUID PRESSURE (bar)


1.9–3.2 2.5


not resistant to penetration of CW agents into their structure, is more challenging. The fixed directional nozzle for spreading LVD-X decontaminant demonstrates a significant difference in decontamination efficiency. Some samples placed in different positions resulted in less homogeneity. Experimental trials with a rotating nozzle and its delivery through a robotized platform are ongoing. This will invariably optimize the results achieved so far. zy


HD


Residual Cont.


(mg.m-2) 0.48


36.75 0.00


5.36


15.16 1.10


LVD-X Decon


efficiency (%)


99.82 60.05


100,00 94.64


91.61 99.39


(Testing panels placed directly in ‘front’ of the LVD-X flow show significantly higher decontamination efficiency compared with ‘side’ samples).


Renato Bonora is Professor of Contaminated Site Remediation, Department of Industrial Engineering, University of Padua. He has worked on CBRN decontamination and detoxification technologies since 1988.


60 CBNW 2013/02


Page 1  |  Page 2  |  Page 3  |  Page 4  |  Page 5  |  Page 6  |  Page 7  |  Page 8  |  Page 9  |  Page 10  |  Page 11  |  Page 12  |  Page 13  |  Page 14  |  Page 15  |  Page 16  |  Page 17  |  Page 18  |  Page 19  |  Page 20  |  Page 21  |  Page 22  |  Page 23  |  Page 24  |  Page 25  |  Page 26  |  Page 27  |  Page 28  |  Page 29  |  Page 30  |  Page 31  |  Page 32  |  Page 33  |  Page 34  |  Page 35  |  Page 36  |  Page 37  |  Page 38  |  Page 39  |  Page 40  |  Page 41  |  Page 42  |  Page 43  |  Page 44  |  Page 45  |  Page 46  |  Page 47  |  Page 48  |  Page 49  |  Page 50  |  Page 51  |  Page 52  |  Page 53  |  Page 54  |  Page 55  |  Page 56  |  Page 57  |  Page 58  |  Page 59  |  Page 60  |  Page 61  |  Page 62  |  Page 63  |  Page 64  |  Page 65  |  Page 66  |  Page 67  |  Page 68  |  Page 69  |  Page 70  |  Page 71  |  Page 72  |  Page 73  |  Page 74  |  Page 75  |  Page 76  |  Page 77  |  Page 78  |  Page 79  |  Page 80  |  Page 81  |  Page 82  |  Page 83  |  Page 84  |  Page 85  |  Page 86  |  Page 87  |  Page 88  |  Page 89  |  Page 90  |  Page 91  |  Page 92  |  Page 93  |  Page 94  |  Page 95  |  Page 96  |  Page 97  |  Page 98  |  Page 99  |  Page 100