"Commercial Systems for the Direct Detection of Explosives
(for Explosive Ordnance Disposal Tasks)"
ExploStudy, Final Report
17/2/2001
Claudio Bruschini
École Polytechnique Fédérale de Lausanne (EPFL) & Vrije Universiteit Brussel (VUB)
Mailing address: EPFL-DI-LAP, INF-Ecublens, CH-1015 Lausanne, Switzerland
Tel.: +41 21 693 3911, Fax: +41 21 693 5263
E-mail:
,
Web: http://diwww.epfl.ch/lami/detec/
This Study has been carried out during the 2nd and 3rd quarters of 2000 on behalf of the Swiss Defence Procurement Agency in Thun (contract No. 155368). Additional financial and logistic support has been received by the Vrije Universiteit Brussel (VUB) and the École Polytechnique Fédérale de Lausanne (EPFL).
Contents: *
1. Introduction: *
6. Acknowledgements: *
7. References: *
8. Websites: *
9. Contacts: *
A1. Other Explosive/Contraband Detection Technologies: *
Systems should preferably be able to make a detection under the following assumptions:
This broader, initial goal did therefore include the
study
of commercially available systems for the direct detection of
explosives,
in sealed (e.g. UXO) as well as non-sealed systems (e.g. "suspicious
objects").
The main conclusions will then again be focussed on the task at hand.
At
first sight bulk explosive detection would seem to be most appropriate
for hermetically as well as some non-hermetically sealed systems,
whereas
trace detection would seem to be most appropriate for non-hermetically
sealed systems. We will try to see in the following up to which extent
this is true.
DISCLAIMER
This report is based on public material.A number of companies or organisations developing and producing explosive detection systems are cited for illustrative purposes. These references are not all-inclusive and do not represent endorsement of the corresponding systems.
A few physical and chemical properties of basic explosives are summarised in Table 1 (the information has been mostly assembled from [YIN99], as well as from [NIJ99a] and [NIJ98]):
| Name | Molecular
Weight |
C | H | N | O | Density
(g/cm3) |
Vapour
Pressure (rel. | Torr) |
Preferred
Trace Det. |
| TNT | 227.13 | 7 | 5 | 3 | 6 | 1.65 | 7.7 ppb | 5.8·10-6 (25 °C) | Particle (Vap.) |
| RDX | 222.26 | 3 | 6 | 6 | 6 | 1.83 | 6.0 ppt | 4.6·10-9 (25 °C) | Particle |
| HMX | 296.16 | 4 | 8 | 8 | 8 | 1.96 | 3.95 ppt | 3·10-9 (100 °C!) | Particle |
| Tetryl | 287.15 | 7 | 5 | 5 | 8 | 1.73 | 7.5 ppt | 5.7·10-9 (25 °C) | Particle |
| PETN | 316.2 | 5 | 8 | 4 | 12 | 1.78 | 18 ppt | 1.4·10-8 (25 °C) | Particle |
| NG | 227.09 | 3 | 5 | 3 | 9 | 1.59 | 0.41 ppm | 3.1·10-4 (26 °C) | Vapour |
| EGDN | 152.1 | 2 | 4 | 2 | 6 | 1.49 | 92.6 ppm | 0.07 (25 °C) | Vapour |
| AN | 80.05 | - | 4 | 2 | 3 | 1.59 | 12 ppb | 9.1·10-6 (25 °C) | Particle (Vap.) |
| TATP | 222.23 | 9 | 18 | - | 6 | 1.2 | ||
| DNB | 168.11 | 6 | 4 | 2 | 4 | 1.58 | 3.8 ppm | 2.9·10-3 (25 °C)* | |
| Picric acid | 229.12 | 6 | 3 | 3 | 7 | 1.76 | 7.6 ppt | 5.8·10-9 (25 °C)* |
TNT (2,4,6-Trinitrotoluene) is one of the most widely used military explosives, and has been in use for about the last 100 years (most of the production during WWI and WWII). DNB (1,3-Dinitrobenzene) was produced in large quantities during WWI (in second place after TNT), and to a lesser extent during WWII. Picric acid (2,4,6-trinitrophenol) has been the third most produced explosive during WWI, and to a much lesser extent during WWII. RDX (Hexogen) is more recent, was the second most produced explosive during WWII and is still in very wide use today, also in plastic explosives. PETN (Nitropenta) is also used in plastic explosives. HMX (Octogen) is a very powerful and costly military explosive, which has been employed in solid-fuel rocket propellants and in military high performance warheads. As general references see also [YIN99, HAA94].Military explosives currently used are mostly a combination of TNT, RDX, PETN, HMX, with a number of organic compounds (waxes, plasticizers, stabilisers, oils, etc.). Examples are Composition B (RDX, TNT), Composition C-4 (or PE 4) (RDX), Detasheet (PETN), Octol (HMX, TNT), Semtex-H (RDX, PETN), etc. [YIN99].
Nitroglycerin (NG) and Ammonium Nitrate (AN, NH4NO3) are used as a basis of other families of explosives (dynamites in the case of NG), typically as high explosive for industrial applications and in solid rocket propellants. Note that pure AN does not contain carbon; it has been widely used to fabricate bombs, but is also widely diffused as a fertiliser. EGDN (Ethylene glycol dinitrate) is a transparent, colourless liquid explosive, which has been used in mixtures with NG for low-temperature dynamites. Its use has greatly decreased due to the replacement of dynamites with ammonium nitrate-fuel oil (ANFO) and slurry explosives [YIN99].
Black powder is a low-order explosive consisting of potassium nitrate (KNO3) or sodium nitrate (NaNO3), charcoal, and sulphur (it does therefore probably not contain hydrogen). It is used in incendiary devices and as low-order high explosive.
Explosives are, as a group, rich in nitrogen and oxygen, poor in carbon and hydrogen, with a particularly characteristic indicator being the oxygen vs. nitrogen atomic density (in mol/cm3, see for ex. Fig. 3.4 [YIN99]). It would nevertheless be necessary, for the application we are considering, to compare the composition of explosives with the inert substances of interest, rather than with the materials commonly employed in security studies (e.g. clothing or plastics, see for example [YIN99]).
Name |
C/O |
H/N |
C/N |
O/N |
Nitrogen |
NG |
0.33 |
1.67 |
1 |
3 |
18.5 |
TNT |
1.17 |
1.67 |
2.33 |
2 |
18.5 |
RDX |
0.5 |
1 |
0.5 |
1 |
38.0 |
PETN |
0.42 |
2 |
1.25 |
3 |
17.7 |
AN |
0 |
2 |
0 |
1.5 |
35.0 |
Table 2: Elemental
ratios for some common basic explosives, derived from Table 1 (last
col.:
[YIN99], Table 3.4)
The vapour pressures for mixtures containing pure explosives, e.g. C-4 containing RDX, may in fact be lower [NIJ99a, YIN99 §2.3] than the values quoted in Table 1 for pure materials, and change from one mixture to the other even if the basic explosive is the same and in the same quantity. Reasons for this include the presence of other substances in the explosive matrix, such as polymeric binders, plasticizers and/or waxes. In addition, in real world situations equilibrium might not be reached due to a number of factors affecting the diffusion and transport of explosive material, such as: packaging and encapsulation, stagnant reflective boundary layer effects, temperature fluctuations, uncontrolled air currents or adhesion of vapour to surrounding surfaces [NAV97, §2.1.2.1.2; NAV9x, NIJ98]. As a result, the actual vapour pressure can be orders of magnitude lower than the values quoted for equilibrium situations [NIJ98], such as those in Table 1. All this obviously affects detection efficiency. On the other hand high vapour pressure impurities might be present, thus potentially facilitating detection.
Vapour pressures are often expressed as relative concentrations in saturated air, rather than in true pressure units, and are usually expressed in units of ppm (parts per million: 1:106, corresponding to one molecule per one million air molecules), ppb (parts per billion, 1:109), or ppt (parts per trillion, 1:1012). Such concentrations are proportional to the true vapour pressure (in torr, or Pascal), as in a given volume and at the same temperature nexpl/nair = pexpl/pair. Indeed, for an ideal gas we have the following relationship between the (vapour) pressure p (in Pascal, with 1 Torr = 133 Pa), the volume V (m3), the quantity of gas n measured in moles (e.g. 1 mole TNT = 227.13 grams), and the absolute temperature T in Kelvin (0 °C ~ 273 K):
pV = nRT => n/V = p/RT
with R being the universal gas constant (8.31 J·mol-1·K-1). The TNT relative concentration at 25 °C for example amounts to 5.8·10-6 torr, or 7.7 ppb, corresponding to about 0.07 ng/cm3 (1 ng = 10-9 g). An order of magnitude figure for TNT of 0.1 ng/cm3 is often encountered. Note that this figure is very small compared to the amount of TNT contained in a typical particle in a fingerprint for example, which might contain several micrograms of TNT (1 mg = 10-6 g = 1000 ng) [NIJ99a].
As we said the vapour pressure increases quite rapidly with temperature; in the case of solid TNT near room temperature for example it approximately doubles every 5 °C. On the other hand this also implies that explosive vapour detection can become difficult in cold environments, see for example [NAV9x]. One way of increasing the chances of a successful vapour detection might therefore be to heat the object (this could however also increase the amount of interfering vapours).
ppm range or
higher:
EGDN and NG
have relatively high vapour pressures (ppm
range or higher), which implies that they and their compounds
(typically
dynamites) are correspondingly "easy" to detect in the vapour phase
with
existing commercial equipment (e.g. of the IMS or ECD type) and also by
the human nose. As a downside of the high vapour pressure, their
particle
detection might also be possible but less effective due to the tendency
of small particles to evaporate rapidly.
ppb range:
TNT and AN
vapour pressures are already in the ppb
range and therefore correspondingly difficult to detect in the vapour
phase,
pushing in many cases the required sensitivity to the detection
system's
limits. Particle detection based on surface swiping is therefore
usually
preferred, with AN being somewhat a special case.
(sub-)ppt
range:
RDX, Tetryl
and PETN and their compounds (in
particular plastic
explosives, and also explosives based on potassium and sodium chlorate)
have a very low tendency to evaporate (ppt
range), with HMX being even a couple of
orders
of magnitude lower (sub-ppt range
at
room temperature). This makes their vapour based detection indeed very
difficult, so that a lot of effort has gone into providing detection of
particulate material instead.
Particle detection itself can be carried out by wiping a surface with a swipe pad, usually provided by the equipment manufacturer himself, which will the be inserted in the instrument's sampling port and be analysed. More details will be provided later on. Sample collection and transport to the detector are therefore indeed key issues [NIJ99b, NAV97]. More details on the factors influencing contact trace detection are provided in [NAV97 §2.1.2.2, NAP99].
| Name | C | H | N | O | Cl | P | As | S | F |
| Lewisite I | 2 | 2 | - | - | 3 | - | 1 | - | - |
| Lewisite II | 4 | 4 | - | - | 3 | - | 1 | - | - |
| Lewisite III | 6 | 6 | - | - | 3 | - | 1 | - | - |
| Clark I (DA) | 12 | 10 | - | - | 1 | - | 1 | - | - |
| Clark II (DC) | 13 | 10 | 1 | - | - | - | 1 | - | - |
| S-Mustard (HD) | 4 | 8 | - | - | 2 | - | - | 1 | - |
| N-Mustard (HN) | 6 | 12 | 1 | - | 3 | - | - | - | - |
| Tabun (GA) | 5 | 11 | 2 | 2 | - | 1 | - | - | - |
| Sarin (GB) | 4 | 11 | - | 2 | - | 1 | - | - | 1 |
| Soman (GD) | 7 | 16 | - | 2 | - | 1 | - | - | 1 |
| VX | 11 | 26 | 1 | 2 | - | 1 | - | 1 | - |
Table 3: Composition of some Chemical Warfare Agents (data source: I.U.T. "GIOS" brochure)
The following Figure provides a useful overview, albeit non-exhaustive, of current Bulk and Trace explosive detection technologies of interest, most of which we are going to discuss in the following.
In the following we will give the priority to the physics behind existing systems or advanced prototypes. For additional interesting comments on bulk explosive detection see also [NAV97, McF80 and McF91, NAP98b].
I = I0e-mlr
where I is the intensity of the emergent beam (photons/s), I0 the intensity of the incident beam, m the total mass attenuation coefficient (describing both absorption and scattering) in cm2/g, l the length of path through the absorbing material (cm), and r the density of the absorbing material (g/cm3). The mass attenuation coefficient m depends on the energy E of the X-rays and on the effective atomic number Zeff of the absorbing material; m decreases for increasing X-ray energy (the beam is less attenuated). Zeff is, for a substance made up of more than one element, the apparent atomic number that results if the substance is treated as if it were composed only of a single element [NIJ99a]. It is closely related to the weighted average of the atomic numbers (Zi) of the constituent elements, i.e. to the average number of electrons per atom.
In the case of X-rays their absorption is basically due to the X-ray's interaction with an atom's electrons, via the photoelectric effect (the X-ray is absorbed and knocks out one of the atom's internal electrons) or via Compton scattering (the X-ray hits an electron and transfers part of its energy to it, therefore continuing with reduced energy). Positron-electron pair production in the field of a heavy atom can occur at high energies, above 1.022 MeV.
All of the X-ray based systems involve irradiation of a target item with X-rays, usually followed by detection of an image created by X-rays that are either transmitted or backscattered by the item. Standard (transmission) X-ray machines have been used for quite a long time, but more in the role of systems to detect weapons and clues to the explosive device such as switches, detonators, wires, etc., rather than the explosive itself [NIJ99a]. Standard airport X-ray machines operate with electron energies of 120 keV impinging on tungsten targets, and the resulting X-ray beam has the characteristic energy of tungsten (~60 keV) [YIN99]. Higher energy machines should be capable of penetrating a few cm (2-3) of steel, and even more for increasing energy.
In order to provide an operator with
identification of
explosives-like substances (high density, low Z material), i.e.
real bulk explosive detection, other X-ray technologies like
backscatter,
dual energy, or computed tomography and combinations thereof have to be
employed. The parameter of interest is actually Zeff, the
effective
atomic number of the screened item (replace in the following paragraphs
Z by Zeff).
Any system that can determine that low-Z materials
are present can have an automated alarmfunction added. A number
of (mostly American) commercial systems are for example listed in Table
6, page 32 of [NIJ99a]. Additional details on X-ray techniques can also
be found in [NIJ98, NAV97].
These systems are mostly used for screening luggage, packages, mail, etc., and most of them are not easily portable. A few are usable for EOD tasks, but not to detect the explosive directly, rather to get information on the object's internal structure, which can already be very useful. See also the comments in Annex A2.1, A2.2.
The behaviour of neutrons in matter depends
strongly on
their kinetic energy. Fast neutrons interact preferentially via
scattering and nuclear reactions (see below). The probability of
reaction
(cross section) for slow neutrons (E<0.5 eV, definitions
vary)
changes instead heavily from one element to the other and according to
the neutron energy, and is determined by individual resonances which
feature
as peaks in the cross section plots. The latter can be very large,
which
indicates a high reaction probability at the corresponding neutron
energy. Thermal
neutrons are a special type of slow neutrons, whose kinetic energy
distribution is in equilibrium with their surrounding (with a typical
energy
of 0.025 eV at room temperature). They move on irregular paths like a
gas
through matter, neither accelerating nor slowing down, scattering quite
a number of times until they are absorbed (captured in the nucleus). In
detail, neutrons can interact with matter in the following ways:
Note that from a biological point of view thermal neutrons are less dangerous than fast neutrons (higher fluxes of thermal neutrons can be tolerated). Fast neutrons have a greater range in target materials and thus allow detection of larger and/or more dense volumes.
All systems of this type, such as Thermal Neutron
Analysis
(TNA) and Fast Neutron Analysis (FNA) as well as their derivatives, are
composed of at least a neutron source to produce the neutrons
that
have to be directed into the target, and a g-ray
detector to characterise the outgoing radiation. The
neutron source can be either a radioactive source or an
accelerator,
possibly moderated (exploiting hydrogen rich substances to slow down
fast
neutrons using elastic scattering):
The neutron generators have reached quite reasonable sizes, still weighing several tens of kilograms, high voltage electronics included, and throughputs of 108 to 109 neutrons/s (for the smaller models). Prices start somewhere around 50 kCHF, but are more in the 100 kCHF range. The ability of pulsing them can be of great advantage in reducing the background signal, allowing for example to differentiate prompt from delayed g-rays (which will occur after the pulse), or g-rays due to inelastic scattering from those due to neutron capture of thermal neutrons. Nevertheless, detecting the g-rays during the pulse can be difficult, depending on the detector and its electronics, in particular for intense pulses. They are commercially available from a few manufacturers such as SODERN in France, http://www.sodern.fr/, MF-Physics in the US, http://www.mfphysics.com/, Schlumberger in the US, http://www.slb.com/emr/generators/, and the Institute of Automatics in Moscow, Russia [RAN99] (plus possibly other Russian sources). Neutron generators are routinely used for other applications such as in the oil exploration industry. Lifetime might have been a problem in the past (currently several 1000 hours?).
Thermal neutrons have to be generated by slowing down (moderating) fast neutrons, as apparently there are no portable means of producing them directly. This process can strongly reduce (by 2 to 3 orders of magnitude) the effective neutron flux, i.e. with respect to what produced by the unmoderated source [VIE99].
Some form of shielding is usually employed, both to screen the detector (from the direct neutrons) as well as the environment and the operator. Nevertheless, in general a respectful distance has to be kept from the source when outside its protective (shielding) case, or from the generator when in use - depending on shielding, from several meters up to 10-20 m say! Note that for the most intense generators activation issues have been reported, i.e. it was preferable to wait a few minutes before approaching again the object under analysis.
The gamma ray detector is another key element of the system. According to the requirements its complexity can range from a simple counting device (registering only the amount of gamma photons) to the measurement of the energy (gamma spectroscopy, essential for chemical characterisation). When the emphasis is on energy resolution - the single spectral lines have to be identified as precisely as possible - the choice often falls onto a HPGe (High Purity Germanium) detector, which has an excellent energy resolution (adjacent spectral lines can usually be very well separated). HPGe has unfortunately the following disadvantages: it is very expensive, its efficiency decreases rapidly with increasing energy (and is in particular very low at the 10.8 MeV nitrogen thermal capture line), and it has to be cooled to low temperatures either cryogenically with liquid nitrogen or electromechanically. Speed might also be an issue. There are therefore situations in which other detectors are preferred, such as BGO (Bismuth Germanate) or NaI (sodium iodide) scintillators, which have a poorer energy resolution (individual spectral lines are "washed out", resulting in overlapping peaks) but can work very fast (high counting rates). These detectors are also much more affordable and do not need cooling. Detector neutron damage might also have to be considered depending on the operating parameters (some detectors are available in "hardened" versions).
The gamma ray spectrum itself can be quite
complex,
according to the target material and the operating conditions (in
particular
for buried targets!). Amongst the factors influencing the signal of
interest
coming from the target object - i.e. the number of g-rays
which are recorded - we schematically have the following:
Most systems need several minutes to reach sufficient statistics to make precise statements. Some elements might be hard to detect due to neighbouring interference lines by other reactions (e.g. O, F, S), or because the energy of the emitted g-ray is low (e.g. As at 280 keV) and therefore more attenuated passing through the container's walls (in particular steel in the case of UXO).
Software is undoubtedly one of the key issues, in particular in presence of complicated spectra as is often the case when using fast neutrons for example, and might need extensive resources even if appropriate hardware is available. According to the system and the task at hand different modes of operations can be envisaged, ranging from the identification of single characteristic spectral lines (peaks) as good indicators for the presence of key elements (chemical weapons for example), to more elaborate spectral deconvolution solutions (extraction of individual peaks from a complicated spectrum).
Broadly speaking, we can define a few typical modes
of operation, in increasing order of overall system complexity:
A list of parameters to be assessed in operational
conditions could include the following:
Concerning the specific subject of humanitarian demining, the International Atomic Energy Agency (IAEA) in Vienna has quite recently started a Co-ordinated Research Project (CRP) on the Application of Nuclear Techniques to Anti-Personnel Landmine Identification. More information is available from the Scientific Secretary, Ulf Rosengard (email: ulf.rosengard@iaea.org, phone: + 43 1 2600 21753). The corresponding reports such as [IAEA99, IAEA00] are a useful source of information on nuclear explosive detection methods.
Table 4 summarises some of the nuclear reactions of interest for the detection/identification of explosives, to which we are going to refer in the following.
| Element | Reactions | Neutron Energy | Reaction Type |
| H | 1H(n,g)2H | Thermal | Prompt |
| C | 12C(n,n'g)12C | Fast (>5 MeV) | Prompt |
| N | 14N(n,g)15N | Thermal | Prompt |
| N | 14N(n,n'g)14N | Fast (>3 MeV) | Prompt |
| N | 14N(n,2n)13N | Fast (14 MeV) | Activation (9.9 min) |
| O | 16O(n,n'g)16O | Fast (>7 MeV) | Prompt |
| O | 16O(n,p)16N | Fast (>9 MeV) | Activation (7.13 sec) |
| Cl | 35Cl(n,g)36Cl | Thermal | Prompt |
| Cl | 35Cl(n,n'g)35Cl | Fast (>3 MeV) | Prompt |
| Cl | 35Cl(n,p)37S | Fast (14 MeV) | Activation (4.9 min) |
Table 4: Nuclear reactions of interest for the detection/identification of explosives (source: [VAL99])
TNA relies on the explosives' elevated nitrogen concentration for their detection, as most of them are nitrated compounds whose nitrogen densities are above those of other materials. One interaction of particular interest is indeed the capture of thermal neutrons on nitrogen, following the reaction 14N(nth,g)15N. The result of this interaction is the production, in about 18% of the cases, of characteristic 10.8 MeV g-rays (the highest g-ray energy produced from a naturally occurring isotope):
14N + n (thermal) ® 15N* ® 15N + g (10.8 MeV)
Nitrogen features also other spectral lines, but it is not clear if and how TNA systems exploit them at present. Hydrogen and most metals (e.g. iron for steel cased UXO) are also easily detected. The capture process on hydrogen produces deuterium (D or 2H) with the release of a characteristic 2.223 MeV g-ray following the reaction 1H(nth,g)2H.
In summary, TNA is able to characterise High Explosives (HE) by their nitrogen and hydrogen signature, possibly exploiting the absence of other elements as well. It is probably the "easiest" among the neutron-based techniques, apart from neutron backscatter. On the other hand it is relatively slow; typical response times range from minutes to tens of minutes, depending on the material being investigated. TNA it is not capable of detecting, in practical terms, neither oxygen nor carbon.
In practice there are several obstacles to be
overcome
to apply TNA successfully for the detection of explosives:
As already indicated in §2.3, thermal neutrons
have to be generated by slowing down (moderating) fast neutrons, as
apparently
there are no portable means of producing them directly. Concerning
possible
thermal neutron sources, the D-T generator is far from optimal for
(pure)
TNA as the 14 MeV neutrons are difficult to shield and produce quite
some
background. In addition, the moderation of 14 MeV neutrons to thermal
neutrons
is apparently quite inefficient. D-D generators, or a radioactive
source
such as 252Cf, seem therefore to be more indicated if the
aim
is to generate a high number of neutrons in the thermal energy region.
Prototype TNA systems are or have been built by companies and organisations such as ANCORE Corp. (formerly SAIC Advanced Nucleonics until the end of 1997) [ANCxx1], Science Applications International Corporation (SAIC US, Santa Clara, CA) [SAI96, BOR00], SAIC Canada [McF98], the Italian INFN (National Institute for Nuclear Physics) EXPLODET collaboration [VIE99], etc. These systems have been mostly targeted at the detection of explosives for security applications, and also as confirmatory sensors for the detection of buried landmines.
A prototype surface and near-surface UXO detector based on TNA has been developed and demonstrated by SAIC [BOR00, ANCxx2, POR99]. It was composed of a Schiebel VAMIDS metal detector array and a TNA sensor head mounted on a remote controlled vehicle, and was tested during the summer and fall of 1996, in Socorro, NM, and at the Yuma Proving Ground, AZ, respectively. During this second occasion the system was fully integrated and capable of scanning, by remote control and with complete coverage, an area of 50x50 m in six hours. The TNA sensor head had a weight of about 150 kg, used a 252Cf radioactive source, and 8 NaI detectors in Socorro (5 minute measurement time) and 12 in Yuma (10 minute measurement time) [POR98].
[BOR00] summarises the results of these tests (as well as of landmine detection tests carried out with similar systems) as follows: "... large antitank mines and large ordnance items buried near the surface can be easily detected with nuclear radiation techniques under realistic field conditions. Smaller mines and UXO items can be detected under more ideal conditions." It is also pointed out that this technique (as well as neutron backscattering) is affected by soil conditions, nonhomogeneity, and burial depth. A detailed analysis of the phenomena involved is carried out in [POR98, POR99, SPA98], including the effect on the signal to noise ratio of the interfering 10.6 MeV capture g-rays from 29Si (which is in fact reported as being the dominant background source in the energy window of interest). The signal to noise ratio, reported to be of the order unity for the tested system, can remain challenging even after background subtraction.
TNA has been successfully applied to the characterization of chemical warfare agents - it is in particular very sensitive to chlorine (see Annex A1.3) - by relying on the detection of characteristic elements, as already mentioned. Some of them are in fact better detectable by exploiting fast neutron inelastic scattering, for example phosphorus which has a thermal neutron capture reaction cross section a factor of 20 lower than chlorine [CAF92b §3.1, DOE92 p. 36].
As already mentioned in §2.3, the energies of the g-rays emitted indicate the elements present in the material. The intensity of the g-rays indicates the relative amount of material present. It is therefore in principle possible to calculate the elemental ratios - how much of each element is present with respect to the others - in order to determine the type of substance under analysis. In the instance of explosives, carbon, nitrogen, and oxygen ratios are considered. Hydrogen (i.e. the proton) cannot be detected by pure FNA.
FNA has therefore the potential of delivering better results than TNA, because it is sensitive to nearly all elements in explosives and opens the possibility of identifying the substance under analysis, but is usually far more complex and expensive. The resulting g-ray spectra can indeed be quite complex as numerous nuclear levels are often excited, especially for 14 MeV neutrons hitting light elements, and even more in the case of buried objects (background due to soil).
Pulsed operations are particularly interesting when using very short fast neutron pulses (typically nanosecond wide, 10-9 sec) - short compared to the flight time across the object to be analysed. In addition, the neutrons have to be as monoenergetic as possible (they have to travel at roughly the same speed). Given these conditions, Time-Of-Flight (TOF) techniques can be used to determine the location of the detected material: the measurement start time is given when the neutron pulse is created, and the stop time when the g-rays are recorded (the g-rays travel at the speed of light, much faster than the neutrons). When combined for example with the vertical scanning of the neutron source and the horizontal movement of the object relative to the source/detector, pulsing provides a three-dimensional spatial resolution capability (still rather coarse but potentially very useful). The nature of the material is again provided by gamma spectroscopy.
Up to now this technique has required rather large installations to produce a neutron beam of the required characteristics (microsecond pulses have been routinely produced in commercial generators, but are obviously much longer than what required for TOF techniques), combined with the need for fast electronics and detectors. Work has been carried out in particular by the ANCORE Corp. (formerly SAIC Advanced Nucleonics, http://www.ancore.com/).
NOTE: The speed v/c of a neutron of kinetic energy K, or actually of any particle, is equal to:
v2/c2 = 1 - m02/m2 = 1 - m02/(m0 + K/c2)2
where m0 is the particle rest mass (939.57 MeV/c2 for a neutron) and m = m0 + K/c2 is its relativistic total mass. A neutron with a kinetic energy of 8 MeV, for example, would therefore have a total mass of 947.57 MeV/c2 (the c2 is in fact usually dropped), and therefore a speed of 0.13·c = 0.39·1010 cm/s = 3.9 cm/nsec, i.e. 13% of the speed of light.
The strength, as well as the weakness, of such a pulsed approach is that the signal to noise ratio improves, but that the overall signal strength is reduced by the duty factor of pulsing, requiring much stronger peak neutron intensity (to compensate for the low duty factor). This in turn can make the spectrum measurement during the pulse very difficult [GOZ96].
The neutron then collides with a nucleus and produces a g-ray, as previously described, whose time of arrival at the detector can be precisely measured [NAV97]. This is therefore again a Time-of-Flight (TOF) technique as described in the PFNA section, allowing to determine the distance travelled by the neutron (as both the speed of the neutron and of the gamma are in principle known). As its direction is also known, three-dimensional spatial resolution of targets can in principle be provided, without the need for scanning. The nature of the volume element of material being analysed is again provided by gamma spectroscopy. Associated Particle Imaging is therefore a technique which can potentially provide 3D information (i.e. voxel by voxel) on the chemical nature of the object under analysis, ideally stoichiometric information (i.e. determination of the quantitative chemical formula: CaNbOc for explosives, where a,b,c are atomic proportions).
Note that the neutron production rate might have
to be
kept low so that neutron interactions do not interfere (need to limit
random
coincidences), depending on the detector and the electronics used; this
would increase measurement time. Some of the neutrons will also loose
part
of their energy in collisions and therefore not be monochromatic any
more,
thus limiting system resolution. The need of having an extra detector
built
in the neutron generator does also not make things easier. This
technique
is therefore far from easy to implement outside of the lab. Research
and
development work has been or is ongoing for example at:
According to official reports, the performance has been verified in the field in real-world situations by the US Army, which has successfully identified hundreds of suspect munitions from burial sites and firing ranges.
MATURITY:
Developed by EG&G ORTEC (now part of Perkin Elmer) and the Idaho National Engineering and Environmental Laboratory (INEEL) at the beginning of the '90s to determine in situ the specific nature of an assortment of containers of munitions and chemical weapons.
AVAILABILITY:
There have apparently been licensing problems a few years ago (difficult to export outside US), which are reported as having been solved. Delivery time quoted at 12 weeks.
COMPLEXITY:
Software seems to be reasonably user friendly. Moderate level of training/education probably required (computer, cryogenics, radiation safety, g-ray spectra).
Two operators for work on the mother dewar (attaching and detaching the detector, etc.).
MOBILITY:
Portable system, can be operated up to 8 hours on internal batteries. Can be transported for field use. Shipped in 5 boxes with a total weight of 280 kg. HPGe detector must be filled with liquid nitrogen every 18 hours [unless electromechanically cooled version employed!].
INFRASTRUCTURE NEEDS:
When detector not in use, it should be attached to a 30-liter "mother" dewar which continuously refills it with liquid nitrogen (two-person team needed).
Detector must be used in a well-ventilated space (> 40 m3), because in case of accident the 1.2 l of liquid nitrogen could expand to 800 l of gaseous nitrogen, displacing enough oxygen in a small room to cause asphyxiation.
Source must be stored after use in approved shipping container at least 5 m away from common human activity.
OPERATIONAL READINESS:
An uncooled detector requires at least 4 to 6 hours on the mother dewar before use. If the detector has been used and is still cold when attached to the mother dewar, it requires only 5 to 10 minutes to refill.
The HPGe detector is also available in an electromechanically cooled version (50x50x50cm compressor, needs mains connection or generator, at least in the version which was discussed; another version is described in [PAR99]).
DETECTION LIMITS & TIMES:
Typical sampling times: 100 to 1000 sec. 2000 sec recommended for HE (155 mm projectile!).
System should be able to identify: Chemical weapons, including nerve agents GA, GB (sarin) and VX; Blister agents HD, HN, HT (mustard gases), and Lewisite; High Explosives (HE) such as composition B, RDX and TNT; military screening smokes such as titanium tetrachloride (FM) and White Phosphorous (WP). Practice munition filled with water, concrete or sand.
PINS sensitivity is the highest for various smoke fills, followed by the CW agents that contain chlorine, and then by CW agents that contain phosphorous. PINS is least sensitive to explosive-filled items (the key element for their identification is N). Sensitivity is greater for large munitions as well as for thin-walled items (e.g. mortar projectiles) [PAR99].
FALSE ALARMS (Rate): TBD (TO BE DEFINED).
OTHER LIMITATIONS / (PERSONAL) COMMENTS:
Primary aim: chemical munition. Detection of HE via detection of H and N. Sensitivity drops rapidly with detector-target distance.
252Cf source can be used for two half-lives (5 years). About 3-5 m exclusion area around the source when in use.
HPGe detector is fragile, has to be handled with care. Detector, source and shielding are usually mounted on a stand for use. How to deal with munition in/on the ground (for the task at hand)?
Software: the relative peak heights (intensities), which are related to the ratios of the elements inside the target (i.e. their concentrations), are apparently also taken in consideration for the final decision-tree based evaluation (library of signatures?). Not clear which nitrogen lines are used.
NOTE: INEEL generally adapts the PINS software for new and unique situations (K. D. Watts, INEEL). INEEL is also currently developing a "mini-PINS" and a neutron accelerator based PINS.
PRICE:
Electromechanically cooled HPGe (as option): +30 kDEM.
TESTING
See References.
REFERENCES:
[CAF92b] A. J. Caffrey, J. D. Cole, R. J. Gehrke, R. C. Greenwood, K. W. Krebs, "Portable isotopic neutron spectroscopy for nondestructive evaluation of CW", in Chemical Weapons Verification, Verification Technologies, Department of Energy/Office of Arms Control and Nonproliferation, 1st/2nd Quarters 1992, DOE/DP/OAC/VT-92A (ref. [DOE92]), pp. 35-39.
[COL93] J. D. Cole, M. W. Drigert, R. Aryaeinejad, A. J. Caffrey, "Nuclear physics in arms control: scenarios, techniques, and results", in Intnl. Symposium on Nuclear Physics of our Times, pp. 322-337, Sanibel Island, FL, Nov. 16-22, 1992. World Scientific, Singapore: 1993.
[CAF94] A.J. Caffrey, et al., "US Army Experience with the PINS Chemical Assay System", INEL report EGG-NRP-11443, Sept. 1994.
[PIN96] PINS Chemical Assay System, User's Manual, Version 2.2, April 8, 1996, EG&G ORTEC.
[PAR99] W. E. Parker, W. M. Buckley, S. A. Kreek, A. J. Caffrey, G. J. Mauger, A. D. Lavietes, "Portable system for nuclear, chemical agent, and explosives identification", in SPIE Proc. Vol. 3769, pp. 43-50, Denver, CO, July 19-23, 1999.
Specifically targeted for the application at hand (differentiating inert UXO from HE filled one). Probe setup - generator vs. detector position/orientation - is flexible.
MATURITY:
Different versions possible, systems starting to be commercialised. Some testing already done, some details in the References.
AVAILABILITY: About 8 months, export licence included (see also Testing).
COMPLEXITY:
Automatic operation via palm-top, from a distance up to 100 m from the probe. PELAN does not routinely display spectra to the operator.
MOBILITY:
Portable system, consisting of the Probe (20 kg, neutron generator head, BGO 3'' x 3'' detector, shielding), Power and Data Module (20 kg, low and high voltage controls, computer), and the palm-top-based Control. Special 10 kg platform provided, if required, for the PELAN-CW (chemical warfare) version. Can be transported for field use.
INFRASTRUCTURE NEEDS:
BGO detector does not necessitate cooling. Power requirements <100 W. System can operate from a shoulder held power pack (not provided) for at least 8 hours, or from a 110V/220V AC source.
OPERATIONAL READINESS: Set-up time of less than 1 hour.
DETECTION LIMITS & TIMES:
Minimal mass: 100 grams of explosives (expected; depends on casing thickness). Typical sampling times: 300 sec (up to 14 min for CW). Inert materials mentioned in the UXO tests: wax-based filling, or red epoxy filling.
FALSE ALARMS (Rate): TBD.
OTHER LIMITATIONS / (PERSONAL) COMMENTS:
Safety distance: larger than 7 m from the Probe [VORxx] (emitted radiation at 15 m is actually below the allowable radiation limits for general public). Neutron generator produces up to 1.6·108 n/s isotropically.
Relies on advanced spectral deconvolution software (broad BGO spectrum with respect to the HPGe detector for example), based on a library of information; have apparently heavily invested in the software development. If the investigation is of same-sized objects under standard geometry conditions, an absolute calibration is possible, and the g-ray counts correspond to a specific elemental concentration. When (as an opposite case) objects under random conditions have to be analysed, if the elemental contents cannot be uniquely determined from the number of counts of each element, elemental ratios such as C/O (up to 10% accuracy), C/N, and C/H are used in a decision making tree. These ratios are reported to allow the differentiation between explosives and innocuous materials, even when the explosives are hidden among other objects (e.g. tools in a tool box, clothing articles, various liquids, etc.).
Residual activation of ordinary materials is reported as minimal since for a 300 s interrogation of an object, neutrons are produced for only 10% of the time. Irradiation of foodstuffs can be calculated based on recent guidelines from the World Health Organization.
Note that an estimation of the background spectrum might have to be acquired via a measurement taken in the vicinity of the target, for example for objects lying on the ground. The C/O ratio is considered as primary. It is not perfectly clear which spectral lines are used for the determination of the nitrogen content, and how robust the system will be in unexpected situations (how much relying on library and geometry? Coping with mixtures?).
PRICE: > 100 K$. Rights granted to a major corporation as from May 2001.
TESTING
The system was field tested in the USA with actual explosives (August 1999). Further testing is planned in Belgium and USA for chemical warfare agent identification (2001). See also the References.
REFERENCES:
[DEP98] L. Dep, M. Belbot, G. Vourvopoulos, S. Sudar, "Pulsed neutron-based on-line coal analysis", J. of Radioanalytical and Nuclear Chemistry, Vol. 234, Nos 1-2 (1998), pp. 107-112.
[VORxx] G. Vourvopoulos, P. C. Womble, "Pulsed fast/thermal neutron analysis: A Technique for Explosives Detection". http://www.wku.edu/API/research/explo.htm
[VOR99a] G. Vourvopoulos, "Method and portable apparatus for the detection of substances by use of neutron irradiation", US Patent No. 5,982,838, Nov. 9, 1999.
[VOR99b] G. Vourvopoulos, P. C. Womble, J.
Paschal, PELAN:
A pulsed neutron portable probe for UXO, IED and landmine
identification,
in Application of Nuclear Techniques to Anti-Personnel Landmines
Identification,
Report of the First Research Co-ordination Meeting held 23-26 Nov. 1999
at the Rudjer Boskovic Institute in Zagreb, Croatia, IAEA publication
IAEA/PS/RC-799.
Contact: Ulf.Rosengard@iaea.org.
[WOM99] P. C. Womble, G. Vourvopoulos, J.
Paschal, P.
A. Dokhale, "Multielement analysis utilizing pulsed fast/thermal
neutron
analysis for contraband detection", in SPIE Proc. Vol. 3769,
pp.
189-195, Denver, CO, July 19-23, 1999.
Targeted at Chemical Warfare Agents and Explosives, in particular via the identification of key chemical elements (for CWA: Arsenic, Bromine, Chlorine, Fluorine, Phosphorus, and Sulphur).
Similar in concept to PINS, replacing the radioactive source with a (unmoderated) D-D generator: about 107 n/s (2.5 MeV), pulse length 20 msec, pulse frequency 10 kHz. Max (overall) power consumption (when applying a liquid nitrogen cooled detector?): 800 W.
Same comments as PINS concerning use of HPGe detector (will not be repeated).
MATURITY (Market):
Starting to market the system for specific applications (esp. CWA).
AVAILABILITY: TBD
COMPLEXITY: User friendly software to identify single elements exists.
MOBILITY:
TBD. For the task at hand power requirements need to be carefully assessed. A jeep is necessary for transportation.
(system portability might be an issue for the task at hand).
INFRASTRUCTURE NEEDS: TBD
OPERATIONAL READINESS: TBD
DETECTION LIMITS & TIMES:
Typical sampling times: 300 sec (for CW). Probably much longer if the detection of nitrogen is required.
FALSE ALARMS (Rate): TBD.
OTHER LIMITATIONS / (PERSONAL) COMMENTS:
Primary aim: chemical munition.
IN pulse detection of P, S, As, F (prompt gamma due to inelastic scattering), OFF pulse detection of Cl, H, N (prompt neutron capture gamma). High detection efficiency due to the reduction of the interference between neutron capture and inelasting scattering reactions has been reported.
Are using D-D after initial experience with D-T (too high energy, D-D makes detection of the key elements just mentioned much easier). Accelerator developed in collaboration with a Russian company. Safety distance: 15 m from generator if no screening present, otherwise (with screening) about 2-3 m. Negligible activation of target object. Generator does not contain tritium.
Bruker has been clear about the non-optimal detection of nitrogen (the system cannot detect carbon nor oxygen, like PINS), i.e. long measuring times, in the standard configuration. Improvements/modifications of the system towards the detection of explosives are therefore under way. A special detector for the detection of nitrogen is being tested. In combination with the pulsed working regime of the generator (low background at the nitrogen gamma energy) good results for the detection of explosives are thus obtained.
Bruker suggested the possibility of trying to identify the inert filler instead of the explosive (when the possible fillers are known a priori), e.g. concrete from the characteristic Al and Si lines.
PRICE: TBD.
Likely to be quite high (with respect to PINS), according to the manufacturer due to the higher use value (e.g. D-D neutron generator). Transportation and storing costs are low because the neutron generator does not contain radioactive substances.
TESTING:
Real tests carried out with a number of chemical munitions (75 mm WWI shells), in collaboration with Tauber Spezialtiefbau GmbH (German EOD company), with positive results (see Refs.).
REFERENCES:
"Zerstörungsfreie Identifikation von
chemischen Kampfstoffen
mit dem Analysensystem NIGAS" (Non-destructive Identification of CWA
with
the NIGAS Analysis System), Bruker Saxonia Analytik GmbH (report), 2000
(?), in German.
Targeted at Chemical Warfare Agents in particular. Developed by WIS (German Armed Forces Institute for Protection Technologies, Munster, Germany).
Similar in concept to PINS, using an AmBe source and somewhat refined electronics (dual ADC converters for high/low gain etc.). Developed own software.
Same comments as PINS concerning use of HPGe detector (will not be repeated).
MATURITY:
?
AVAILABILITY:
Interesting system, which WIS does not sell; it has granted rights to a small company (Hazard Control). The latter made it in fact clear that A) the system still has to be ruggedised for field use, B) there is no market for individual units.
COMPLEXITY:
Software seems to be reasonably user friendly. Moderate level of training/education (computer, cryogenics, radiation safety, g-ray spectra) probably required.
MOBILITY:
All parts and transportation boxes portable by 2 persons.
INFRASTRUCTURE NEEDS:
Source must be stored after use in approved shipping container...
OPERATIONAL READINESS: Set up time of less than 1 hour (if detector already operative).
DETECTION LIMITS & TIMES:
Typical sampling times: 1 to 30 min, depending strongly on the amount of agent present and the steel wall thickness of the container. About 10 min for a 155 mm shell.
No problem to detect H, Cl and As; for the other elements (P, S, F), the detection sensitivity is lower and/or the detection is complicated by interfering gamma lines from other reactions. The system is able to identify to some extent, with longer detection times, also C and O (the neutrons produced by the AmBe source have a higher average energy than those from 252Cf) and N.
FALSE ALARMS (Rate): TBD.
OTHER LIMITATIONS / (PERSONAL) COMMENTS:
Primary aim: chemical munition. Collaboration with OPCW inspectors. HE not widely tested, nor (partially) buried objects. Possible minimal explosive detectable mass of 1 kg (depends on steel casing thickness and geometry)?
The volume analysed by the system is estimated to be about a half-sphere of 10 cm radius centred around the detector surface.
WIS suggested the possibility of using only BGO or NaI if the aim is only to detect nitrogen (more efficient at higher energies).
PRICE: TBD.
TESTING
The DGA/DCE/CEB (Centre d'Études du Bouchet of the Délégation Générale à l'Armement, the French Defence Procurement Agency) has a NIPPS system available, which has been tested with positive results [VET98] on WWI projectiles (1997). The latter are characterised by a lot of different geometries and compositions. The analysis of WWI munition is indeed not a simple task (wide number of configurations, several hundred different types, much testing was done at the time).
Note that explosives were usually identified by the absence of P or Cl rather than by nitrogen detection (but "only" a 30% efficiency HPGe detector was used). Results do quite depend on the casing thickness.
REFERENCES:
[VET98] F. Vettese, B. Asselineau, C. Pienne, F.-W. Buchholz, L. Schänzler, G. Tumbrägel, "Old Munition Identification by Neutron Interrogation Assessment of the German NIPPS System", in Proc. 6thInternational Symposium on Protection Against C & BW Agents, Stockholm, 1998.
Conceived as a modular system, with D-T generator or AmBe source, HPGe or NaI detector, different types of shielding, according to the exact needs.
Uses the portable (gamma) spectrometer NOMAD PLUS by EG&G ORTEC (now Perkin Elmer).
Same comments as PINS concerning use of HPGe detector (will not be repeated).
MATURITY:
A real commercial version does not exist yet. Part of the software would have probably to be modified or specifically written for the task at hand (the currently used software is a standard package from EG&G for the analysis of g-ray spectra).
DETECTION LIMITS & TIMES:
Standard measurement time of 400 sec with D-T generator, but really depends on application.
OTHER LIMITATIONS / (PERSONAL) COMMENTS:
Safety distance: 10-20 m when generator in use, which probably produces up to 108 n/s, 12 Hz pulse repetition frequency, 1.5 msec pulse length (very intense pulses). Wait 10-15 min after the end of the measurement (activation of metallic objects!). AmBe radioactive source more indicated when thermal neutrons are required.
PRICE: TBD.
TESTING
I.U.T. has definitely practical experience in the analysis of munition and the discrimination of chemical vs. High Explosive (HE) vs. inert munition, looking at a number of different parameters. The system was however operated by a specialist (i.e. I.U.T. provided a service to Koch Munitionsbergungsgesellschaft mbH, a German EOD company). Some of the parameters which were looked at included the H/O vs. Si/O ratio (the inert shells were either empty, or contained concrete or silica sand), the oxygen peaks with respect to each others as well as their importance in the overall spectrum, etc. C/O, C/N ratios not considered up to now.
Other applications included the need to determine if a given substance was present or not in the object under analysis.
REFERENCES:
Targeted at Chemical Warfare Agents, in particular old WWI munition.
Similar in concept to the previously mentioned systems (e.g. GIOS), using a SODERN GENIE 16 pulsed D-T generator as source (2·107 n/s), and a "modified" NIPPS detection system.
Same comments as PINS concerning use of HPGe detector (will not be repeated).
DETECTION LIMITS & TIMES:
Typical sampling times: 10 min.
OTHER LIMITATIONS / (PERSONAL) COMMENTS:
Primary aim: chemical munition.
The volume analysed by the system is estimated to be about a half-sphere of 10 cm radius centred around the detector surface.
DGA does not sell/market the system itself. In the best case it can sell the technical specifications (how to assemble it).
The detection of prompt g-rays due to the impinging fast neutrons is carried out during the pulse, i.e. in coincidence with it, and is partially perturbed by the pulse itself (the detector is partially "blinded" during the neutron pulse). The detection of capture g-rays, carried out in anticoincidence with the neutron pulse, profits on the other hand from a reduced noise level and features therefore a sensitivity higher than the one offered by radioactive source based systems.
TESTING
System was tested by DGA/DCE (1998-99) on 50 WWI projectiles of different calibre, contents and origin (large variations are characteristic of WWI munition) with positive results [VET99]. A previous test on simulated 75 mm French projectiles (8 mm thickness) resulted in N and Sn being difficult to detect, and C quite impossible (all other elements of interest were easily identified), within the 10 minute measurement time.
Conventional High Explosives munition has been identified by an excess of oxygen combined with the absence of key CWA elements. Direct identification using nitrogen detection, characteristic of HE, has been possible only in a few cases.
The electronics could be improved (made faster), the software too.
REFERENCES:
The Neutron Source consists of a compact pulsed and ultra fast plasma neutron source. It is able to generate 108 high-energy neutrons (energy greater than 8 MeV) per 10 nanosecond pulse (pulses are very short!). The source is non-radioactive when switched off and has a low power requirement, less than 150 W. Time-of-Flight Analysis (TOF) is therefore also possible: it consists in measuring the time interval between two events, and therefore the particle's range - how far the particle has travelled - knowing its speed.
Measurement of the outgoing g-rays is carried out by a set of special purpose, low cost large area gamma detectors, with a very fast response time, less than 2 nsec. Measurements are concurrently possible over several different spectral channels (energy bands), and efficiency limiting pile up effects, due to two or more particles arriving too close in time, have been resolved by operating the detectors in current mode, instead of the traditional method of pulse counting.
In the end it is possible to obtain a distinct signature which characterises the elemental proportions - how much of each element (C, H, N, O) is present with respect to the others - in order to determine the substance type. This is implemented using novel data processing algorithms capable of extracting an explosive's features with only a few detection channels.
Locating the substance's position (in case of a buried object) should also be possible using triangulation methods, that is by knowing an estimate of the substance's distance along a direction and looking at the ground from several different directions.
[Source: EUDEM trip report, March 1999, Unpublished; revised Dec. 2000]
Laboratory tests are foreseen for the end of
2000,
with a prototype ready at the beginning of 2001.
Concerning similar applications, they have
furnished D-T
generators to INEEL (for PINS), the DGA for the analysis of chemical
weapons
(see the description of the NICEB system), and the French police.
The potentialities of the "Atometer" API-TOF system by Maglich and colleagues [MAG00] are also acknowledged (see also §2.3.5); the system is however still is in a development phase.
The use of a time-tagged radioactive source
represents
also an interesting development: a time trigger is provided when
neutrons
are emitted, which in laboratory tests allowed to reduce the background
signal and enhanced the overall performance of a neutron backscatter
system
for landmine detection [CRA00].
Improvements/modifications of the system towards the detection of nitrogen could also be envisaged, at hardware as well as at software level (use of a more efficient detector for example, e.g. larger HPGe or even NaI/BGO, adaptation of current software, improved measurement setup). Note that in the case of PINS the possibility of adapting the existing software "for new and unique situations" has been explicitly mentioned by K. Watts, INEEL.
An alternative is represented by the NIPPS system (WIS/Hazard Control) that employs an AmBe radioactive source (but the detection of oxygen is probably not easy given the energy spectrum).
| Acronym | Detector Type |
| Colour | Colour Change of Test Paper |
| ECD | Electron Capture Detector |
| FIS | Field Ion Spectrometer |
| GC/CL | Gas Chromatograph / ChemiLuminescence |
| GC/ECD | Gas Chromatograph / Electron Capture Detector |
| GC/IMS | Gas Chromatograph / Ion Mobility Spectrometer |
| GC/MS | Gas Chromatograph / Mass Spectrometer |
| GC/SAW | Gas Chromatograph / Surface Acoustic Wave |
| IMS | Ion Mobility Spectrometer |
| ITMS® | Ion Trap Mobility Spectrometer (pat. Ion Track Instruments) |
| TR | Thermo-Redox |
Table 5: Trace explosive detection technologies and their acronyms (source: [NIJ99a], Table 3)
In swipe collection, a sampling pad (usually supplied by the manufacturer), usually paper or cloth [NIJ98], is wiped across a surface suspected of having residue of explosive material; direct contact is therefore required. This surface could be a tabletop, the outside of a package, a piece of luggage, clothing, and so forth. The sampling pad is then inserted into a sampling port on the instrument for thermal desorption and subsequent analysis. Particle detection is also discussed in some detail in [NAV9x, YIN99].
In contrast, vapour collection involves the use of a small hand-held vacuum cleaner to collect airborne vapours or particles. Typically, vacuuming is performed just above the surface to be investigated. A collection filter (or a pre-concentrator) is located inside the inlet of the vacuum, and air is drawn through this filter. The explosive material (actually in the form of either vapour or particles, see also [NAV9x]) will be trapped on the filter. The filter is then removed and analysed by the system in a manner similar to the analysis of a swipe sample. Vapour sampling of this sort is generally less sensitive than swipe sampling, but is for example advantageous for screening people because it is not necessary to touch the person being screened (taking samples with vapour collection is regarded as less invasive than collecting swipe samples).
Sample acquisition is identified in [NAV97, NAV9x] as the primary weakness of current trace detection systems, rather than detector sensitivity, for the applications therein discussed. See also [ROU97b]. An interesting discussion and critical analysis of vapour vs. particle explosive detection is also carried out in the [NAV9x] report.
Note that all trace gas detectors can be used with preconcentrators, which essentially act as gain amplifiers [McF91]. Their efficiency is somewhat constrained for practical applications by the need to keep a reasonable measuring time, in particular in the case of real-time systems. On the same topic see also [YIN99, McF80].
Trace detection of UXO seems to be possible, at least in some circumstances, as application of dogs would seem to testify (for example during demining operations), so that the same might be true for their characterization (inert or not). However, we can anticipate that there does not seem to be a lot of material available on this subject, let alone a commercial system. We will therefore turn our attention to work in similar fields (e.g. landmine detection), as well as to some R&D work concerning more specifically the UXO problem.
This work tells us that in the case of landmines some explosive vapour emission is indeed likely to occur gradually from leaks in the casing or through seals and seams, and/or from evaporation of the residual explosive found on the surface of the casing [DES98]. The soil could also be contaminated with trace quantities of explosives during the burial process (but this looks less likely to be applicable to the scenario we are considering).
Detailed results of modelling activity are for example described in [PHE98, GEO99, WEB99]. It is particularly interesting that explosive compounds such as TNT, DNT and RDX will have (for the given assumptions) over 90% of the mass fraction adsorbed to the soil solid phase, up to 10% present in the soil aqueous phase, and less than 10-6 in the soil vapour phase. The effect of parameters such as burial depth, how long the mine has been buried (time lag), biochemical half-life of explosives, location and climatic conditions, uptake by plant roots, soil moisture, etc., have also started to be addressed.
The importance of 2,4-DNT and 1,3-DNB vapours (explosive related chemicals) for the detection of landmines has also been stressed, as they can be majoritary with respect to (2,4,6-)TNT [GEO99]. Some authors estimate the concentration of TNT in air over a landmine as being a factor 103-106 below the equilibrium vapour concentration, which would mean ppt (part per trillion, 1:10-12) to ppq (parts per quadrillion, 1:10-15) sensitivity necessary to detect TNT in the vapour phase (!).
Providing realistic figures for explosive vapour concentrations is indeed not easy, as the vapour losses are difficult to estimate. For comparison, in the case of IEDs [McF91] quotes a "crude" upper limit of 1 ng/m3 (m3, not cm3!) for the minimum sensitivity necessary to detect TNT (which would be about a factor 105 lower than what expected from the vapour pressure alone, corresponding to 0.1 ppt). The most sensitive technique quoted in the same report was atmospheric source mass spectrometry, in particular APCI MS (Atmospheric Pressure Chemical Ionization Mass Spectrometry). It was deemed sufficiently sensitive even without the use of preconcentrators, whereas atmospheric source tandem mass spectrometry (MS/MS) was deemed marginally feasible without preconcentrators and feasible with one, and IMS was deemed feasible with a preconcentrator. All estimations were based on the previously quoted limit. A number of other studies have been certainly carried out since.
Sample acquisition is again a key issue. Improved sampling devices have been proposed [YIN99], for example in [FIS98] for particles, in [CHR99, GEH99, GEI99] for vapours. Building soil probes to extract the explosive compounds adsorbed on soil particles and/or dissolved in the soil water is also an attractive option, if operationally feasible.
In 1997 the US Defense Advanced Research Projects Agency (DARPA) started a 3-year technology development program to detect mines via their chemical signature ("Dog's Nose Program"). The results of these extensive efforts are detailed at http://www.darpa.mil/ato/programs/uxo/.
The Sandia National Labs have carried out work with the objective of developing a field portable chemical sensing system to examine mine-like objects and UXO in near-real time. Field tests have included unearthed mortar rounds and artillery shells, and AP/AT mines on land [ROD00]. One sampling system was designed for soil vapour sampling, another for sampling exposed munitions, the latter consisting of a battery-powered pump and a short quartz tube; the explosive is then thermally desorbed into an Ion Mobility Spectrometer. The chemical sensing systems are capable of sub-ppb detection of TNT and related explosive compounds.
UXO exposed to the environment was analysed to determine whether they were inert or contained explosives (July 1998, Cape Cod, MA): a total of 1112 projectiles, including 60 mm mortars, 81 mm mortars, and 105 mm artillery shells were analysed, along with 151 pieces of scrap ordnance, partial fuses and other items. The UXO showed a significant amount of corrosion. The samples were collected along seams, joints, and where breaches in the case could be observed. As most shells were expected to be inert, they were analysed in groups of 25, with a sampling time of 125 seconds per group. If a signal was observed, the shells in the corresponding grouping would be re-analysed individually. All 1263 items were sampled in three days.
Every shell was cut open to verify the contents. Overall the vast majority were found to be inert. The vapour analysis did not produce any false positives (i.e. false alarms), but two false negatives (two intact 105 mm shells which were found to be live and for which no IMS signal was registered, for unknown reasons). Additionally, ten 105 mm shells believed to contain explosives were analysed at Sandia. All produced detectable signals and were correctly identified. For details on the landmine field tests see also [CHA99]. They allowed to prove the ability to detect explosive molecules in soil samples in the vicinity of buried land mines.
INEEL (Idaho National Engineering and Environmental Laboratory) has carried out tests on new munitions at Dugway Proving Grounds to determine if explosive vapours could be detected outside them. Explosives were not detected using IMS technology. INEEL continues to develop methods to sense very low levels of explosive vapour near munitions.
[INEEL is also developing a mobile Secondary Ion Mass Spectroscopy (SIMS) system for the detection of trace chemicals on surfaces, with a system being currently deployed on an Army's system and undergoing evaluation. Laboratory based SIMS systems are currently used at INEEL to detect very low levels of chemicals on surfaces. Explosives are more difficult to detect than chemical warfare agents. SIMS has been tested at the Army's facilities at Dugway Proving Grounds. SIMS can be optimised for explosives detection.]
We can summarise our findings as follows:
Nearly no such system is as yet really available off-the-shelf, perhaps apart from PINS, and capable of working under all the assumptions listed in the Introduction. It should nevertheless be possible to identify one or more systems meeting most of the requirements.
"Simple" bulk detection systems such as neutron or gamma backscatter, already used for security applications, could perhaps also be useful in selected scenarios.
Note that US public documents such as the NAP publications, the NAVEODTECHDIV reports, or the NIJ reports, are in general quite open in the discussion of (trace) explosive detection systems.
Bulk detection is interesting on paper but far from being easy to apply in practice, in particular when looking for small quantities hidden in a complex matrix, with possible interferents being present as well. Neutron based systems are hampered by radiation hazard, NMR/NQR devices are screened by metallic enclosures. Detection times can also be too long to be practicable, depending on the application.
[McF91] J. E. McFee, Y. Das, Advances in the Location and Identification of Hidden Explosive Munitions, Defence Research Establishment Suffield, Report No. 548, Feb. 1991, 83 pp.
[NAV97] Requirements Analysis and Technology Assessment for Portable Explosive Detectors, Naval Explosive Ordnance Disposal Technology Division (NAVEODTECHDIV), Indian Head, MD, USA, 14 April 1997. http://www.uxocoe.brtrc.com/TecReports.htm
[NAV9x] The Naval Explosive Ordnance Disposal
Technology
Division Results of Explosive Detection Research in Support of Portable
Explosive Detection, Naval Explosive Ordnance Disposal Technology
Division
(NAVEODTECHDIV), Indian Head, MD, USA (unknown date, possibly 1997).
http://www.uxocoe.brtrc.com/TecReports.htm
[NAV00] Catalog of Explosive Detection Equipment,
Naval
Facilities Engineering Service Center, Security Engineering Division,
Department
of the Navy Explosive Detection Equipment Program, 1100 23rd Avenue,
Port
Hueneme, CA 93043-4370.
http://www.explosivedetection.nfesc.navy.mil/
-> EDE Catalog -> Catalog (last update 3/1/2000). Same starting
address
for the "Vendor List".
[NIJ98] D. W. Hannum, J. E. Parmeter, Survey of Commercially Available Explosives Detection Technologies and Equipment, written for the The National Law Enforcement and Corrections Technology Center, a Program of the National Institute of Justice, National Institute of Justice, September 1998, NCJ 171133. http://www.explosivedetection.nfesc.navy.mil/ -> EDE Catalog -> Survey, or directly http://www.nlectc.org/pdffiles/expsurvey.pdf
[NIJ99a] C. L. Rhykerd, D. W. Hannum, D. W. Murray,
J.
E. Parmeter, Guide for the Selection of Commercial Explosives Detection
Systems for Law Enforcement Applications, NIJ Guide 100-99, National
Institute
of Justice, Office of Science and Technology, Washington, DC 20531,
September
1999, NCJ 178913. http://virlib.ncjrs.org/LawEnforcement.asp
or directly
http://www.ncjrs.org/pdffiles1/nij/178913-1.pdf
and http://www.ncjrs.org/pdffiles1/nij/178913-2.pdf
[STE98] J. I. Steinfeld, J. Wormhoudt, "Explosives Detection: A Challenge for Physical Chemistry", Annu. Rev. Phys. Chem., vol. 49, pp. 203-232, 1998.
[YIN99] J. Yinon, Forensic and Environmental Detection of Explosives. Chichester, UK: John Wiley & Sons, 1999.
[DOE92] Chemical Weapons Verification, Verification Technologies, Department of Energy/Office of Arms Control and Nonproliferation, 1st/2nd Quarters 1992, DOE/DP/OAC/VT-92A.
[EXPL99] NVESD/JUXOCO Explosive Detection Workshop, NVESD (Night Vision and Electronic Sensors Directorate), Ft. Belvoir, VA, 25-27 August 1999. http://www.uxocoe.brtrc.com/workshp.htm -> Detection
[JPL95] Sensor Technology Assessment for Ordnance
and
Explosive Waste Detection and Location, JPL D-11367 rev B, March 1,
1995.
Prepared by the Jet Propulsion Lab (JPL), Caltech, Pasadena, CA, for
the
U.S. Army Corps of Engineers, Huntsville Division, Huntsville, AL, and
Army Yuma Proving Grounds, Yuma, AR.
To be requested from Ms E. Moorthy, Archives and
Records,
JPL, phone +1 818 397-7952 (fax 7121), E-mail:
elizabeth.a.moorthy@jpl.nasa.gov,
$32.40 (Sept. 1996 information).
[NAP98a] BLACK AND SMOKELESS POWDERS: Technologies
for
Finding Bombs and the Bomb Makers, Committee on Smokeless and Black
Powder,
Board on Chemical Sciences and Technology, Commission on Physical
Sciences,
Mathematics, and Applications, National Research Council. ISBN
0-309-06246-2,
National Academy Press, Washington, D.C. 1998.
http://books.nap.edu/html/smokeless/
[NAP98b] Containing the Threat from Illegal
Bombings:
An Integrated National Strategy for Marking, Tagging, Rendering Inert,
and Licensing Explosives and Their Precursors, Committee on Marking,
Rendering
Inert, and Licensing of Explosive Materials, Board on Chemical Sciences
and Technology, Commission on Physical Sciences, Mathematics, and
Applications,
National Research Council. ISBN 0-309-06126-1, National Academy Press,
Washington, D.C. 1998.
http://books.nap.edu/books/0309061261/html/R1.html
Appendix F contains also a report of a visit carried out in 1997 by the report's authors to the Swiss Scientific Research Service. Background information about the Swiss situation and experience with tagging of explosives is provided, as well as the corresponding conclusions about the efficacy of the strategy chosen to control harmful and illegal uses of explosives.
[NAP99] Assessment of Technologies Deployed to
Improve
Aviation Security: First Report, Panel on Assessment of Technologies
Deployed
to Improve Aviation Security, National Materials Advisory Board,
Commission
on Engineering and Technical Systems, National Research Council,
Publication
NMAB-482-5. ISBN 0-309-06787-1, National Academy Press, Washington,
D.C.
1999.
http://www.nap.edu/catalog/9726.html
[NIJ99b] G. A. Eiceman, C. M. Boyett, J. E. Parmeter, Evaluation of a Test Protocol for Explosives Trace Detectors Using a Representative Commercial Analyzer, NIJ Report 100-99, National Institute of Justice, Office of Science and Technology, Washington, DC 20531, September 1999, NCJ 178261. http://virlib.ncjrs.org/LawEnforcement.asp or directly http://www.ncjrs.org/pdffiles1/nij/178261.pdf
[YIN93a] J. Yinon (Ed.), Advances in analysis and detection of explosives (proceedings of the 4th International Symposium on Analysis and Detection of Explosives, Sept. 7-10, 1992, Jerusalem, Israel). Dordrecht: Kluwer, 1993.
[YIN93b] J. Yinon and S. Zitrin, Modern methods and applications in analysis of explosives. Chichester, UK: Wiley, 1993.
[SAL99] S. H. Salter, Report on the Hidden Explosives Workshop, Rovereto, Italy, June 1999, 6 pp. Contact: shs@mech.ed.ac.uk.
[HAA94] R. Haas, G. Möschwitzer,
Rüstungsaltlasten
- ein kommunales Problem, in Hermanns/Walcha (Eds.): Ökologische
Altlasten
in der kommunalen Praxis. Aufgaben der Kommunalpolitik, Band 11,
Deutscher
Gemeindeverlag, Köln, 1994 (in German).
http://haas.purespace.de/V16.html
or from http://haas.purespace.de/start.html
-> Übersicht: Rüstungs-altlasten
[ROS91] D. H. Rosenblatt, E. P. Borrows, W. R. Mitchell, D. L. Palmer, "Organic Explosives and Related Compounds", The Handbook of Environmental Chemistry, Vol. 3, Part G, Ed 0 (May 24th, 1991), pp. 195-234.
[ROU97a] A. M. Rouhi, "Land Mines: Horrors Begging For Solutions", Chemical & Engineering News, vol. 75, no. 10, pp. 14-22, March 10 1997. http://pubs.acs.org/hotartcl/cenear/970310/land.html.
[ROU97b] A. M. Rouhi, "Detecting Illegal
Substances",
Chemical
& Engineering News, Sept. 29 1997.
http://pubs.acs.org/hotartcl/cenear/970929/detect.html.
[BRO96] D. R. Brown, T. Gozani, "Thermal neutron analysis technology", in SPIE Proc. Vol. 2936, pp. 85-94, Boston, MA, Nov. 19-20, 1996.
[GOZ96] T. Gozani, "Inspection techniques based on neutron interrogation", in SPIE Proc. Vol. 2936, pp. 9-20, Boston, MA, Nov. 19-20, 1996.
[VIE99] G. Viesti (for the EXPLODET collaboration), "Il ruolo delle tecniche nucleari nella rivelazione di mine ed esplosivi nascosti" (in Italian), Università degli Studi di Padova, Dipartimento di Fisica, Pubb. DFPD 99/NP/41, Sept. 1999.
A number of institutions carrying out trace explosive detection research, and with which it might be worthwhile to stay in contact, have already been mentioned in §4.2.1 and §4.2.2.BULK Expl. Detection of Landmines and/or UXO:The DGA (Délégation Générale à l'Armement, the French Defence Procurement Agency) has been working to understand the potential of neutron based systems for the characterization of chemical weapons (F. Vettese <frederic.vettese@etca.fr>, DGA/DCE/CEB). DGA/SPART (Service des Programme d'Armement Terrestre) has launched in the year 2000 an invitation to tender concerning a "Feasibility study for a landmine confirmation system based on neutron interrogation".
The EOD requirements of the NAVEODTECHDIV (Naval Explosive Ordnance Disposal Technology Division, Indian Head, Maryland) are probably quite similar to those of other Institutions/Organisations, e.g. :
UXO: Confirmatory sensor for fill. Discriminate between inert, explosive and other fills. IEDs: Go/no-go gage. Assist in disruption/render safe mission.
[ANCxx2] Thermal Neutron Analysis Sensor for
Mine/UXO
Detection, ANCORE Corporation (formerly SAIC Advanced Nucleonics),
Santa
Clara, CA (copy of presentation).
Contact: Douglas Brown <doug@ancore.com>.
[BOR00] G. M. Borgonovi, R. O. Ginaven, V. J. Orphan, Landmines and Unexploded Ordnance Detection, in A Remotely Controlled Multi-Sensor Platform for Humanitarian Demining, Report of the Advisory Group Meeting held 3-7 April 2000 at the IAEA Headquarters, Vienna, Austria, IAEA publication IAEA/PS/AG-1093.
[BYS00] V. M. Bystritsky, et al., "Experiments on Identification of Hidden Substances with Detection of Particles Associated with Neutron Probing", in Proceedings 4th Intnl. Symposium on Technology and the Mine Problem, Naval Postgraduate School, Monterey, CA, Mar. 13-16, 2000.
[CRA00] R. A. Craig, A. J. Peurrung, D. C. Stromswold, "Mine Detection using Timed Neutron Moderation", in Proc. UXO Forum 2000, Session 10 (Detection), Anaheim, CA, May 2-4, 2000.
[HOL00] D. Holslin, J. Reed, "Transportable Inspection System for Mine Confirmation", in Proceedings 4th Intnl. Symposium on Technology and the Mine Problem, Naval Postgraduate School, Monterey, CA, Mar. 13-16, 2000.
[HUS99] E. M. A. Hussein, What can an Isotopic Neutron Source provide for Landmine Detection? A Monte Carlo Study, in Application of Nuclear Techniques to Anti-Personnel Landmines Identification, Report of the First Research Co-ordination Meeting held 23-26 Nov. 1999 at the Rudjer Boskovic Institute in Zagreb, Croatia, IAEA publication IAEA/PS/RC-799. Contact: Ulf.Rosengard@iaea.org.
[IAEA99] Application of Nuclear Techniques to
Anti-Personnel
Landmines Identification, Report of the First Research Co-ordination
Meeting
held 23-26 Nov. 1999 at the Rudjer Boskovic Institute in Zagreb,
Croatia,
IAEA publication IAEA/PS/RC-799.
Contact: Ulf.Rosengard@iaea.org.
[IAEA00] A Remotely Controlled Multi-Sensor Platform
for
Humanitarian Demining, Report of the Advisory Group Meeting held 3-7
April
2000 at the IAEA Headquarters, Vienna, Austria, IAEA publication
IAEA/PS/AG-1093.
Contact: Ulf.Rosengard@iaea.org.
[MAG00] B. C. Maglich, et al., "Development of Atometer Model GammaNose™ for Humanitarian De-mining: ...", in Proceedings 4th Intnl. Symposium on Technology and the Mine Problem, Naval Postgraduate School, Monterey, CA, Mar. 13-16, 2000.
[McF98] J. McFee, et al., "A Thermal Neutron Activation System for Confirmatory Non-metallic Land Mine Detection", in SPIE Proc. Vol. 3392, pp. 553-564, Orlando, FLA, April 13-17, 1998.
[MOL85] R. B. Moler (Ed.), Workshop Report: Nuclear Techniques for Mine Detection Research (sponsored by Belvoir Research and Development Center, Ft. Belvoir, VA), Lake Luzerne, New York, July 22-25, 1985. DTIC Ref. AD-A167 968.
[MOL91] R. B. Moler (Ed.), Technical Report: Nuclear and Atomic Methods for Mine Detection, Department of the Army, Belvoir Research, Development and Engineering Center, Ft. Belvoir, VA, Nov. 1, 1991. DTIC Ref. AD-A243 332.
[POR98] L. J. Porter, D. A. Sparrow, J. T. Broach, R. Sherbondy, J. Bendahan, "Assessment of thermal neutron analysis applied to surface and near-surface unexploded ordnance detection", in SPIE Proc. Vol. 3392, pp. 533-544, Orlando, FLA, April 13-17, 1998.
[POR99] L. J. Porter, "The use of thermal neutron analysis in unexploded ordnance and mine detection", in SPIE Proc. Vol. 3769, pp. 126-140, Denver, CO, 19-23 July, 1999.
[RON00] T. J. Roney, R. J. Pink, T. A. White, M. Smith, K. Shetterly, "Digital Radiography and Computed Tomography of Chemical Munitions: Development and Implementation of Field Inspection System", in Proceedings 4th Intnl. Symposium on Technology and the Mine Problem, Naval Postgraduate School, Monterey, CA, Mar. 13-16, 2000.
[SAI96] Vehicular Mine Detection Testbed, Final Scientific & Technical Report-A0002, Test/Inspection Report-A004, Contract No. DAAB12-95-C-0030, SAIC (Scientific Applications International Corporation), Santa Clara, CA, April 16, 1996.
[SPA98] D. A. Sparrow, L. J. Porter, J. T. Broach, R. Sherbondy, "Phenomenology of prompt gamma neutron activation analysis in the detection of mines and near-surface ordnance", in SPIE Proc. Vol. 3392, pp. 545-552, Orlando, FLA, April 13-17, 1998.
[VAL99] V. Valkovic, A Feasibility Study of Landmines Detection using 14 MeV Neutrons, in Application of Nuclear Techniques to Anti-Personnel Landmines Identification, Report of the First Research Co-ordination Meeting held 23-26 Nov. 1999 at the Rudjer Boskovic Institute in Zagreb, Croatia, IAEA publication IAEA/PS/RC-799. Contact: Ulf.Rosengard@iaea.org.
NOTE: Proceedings of the 4th Intnl. Symposium on Technology and the Mine Problem are available on CD-ROM. Produced by DMC Meeting Management (http://www.dmc2000.com/), contact: Carol Killip carol@dmc2000.com.
[CHA99] W. Chambers, J. Phelan, P. Rodacy, S. Reber, R. Woodfin, "Explosive Ordnance Detection in Land and Water Environments with Solid Phase Extraction/Ion Mobility Spectrometry", in SPIE Proc. Vol. 3710, pp. 290-298, Orlando, FLA, April 5-9, 1999.
[CHR99] M. Christensson, P. Gardhagen, "A new portable biosensor technology for area reduction", in SPIE Proc. Vol. 3710, pp. 335-342, Orlando, FLA, April 5-9, 1999.
[DES98] S. Désilets, L. W. Haley, U. Thekkadath, "Trace
explosive
detection for finding landmines", in SPIE Proc. Vol. 3392, pp. 441-452,
Orlando, FLA, April 13-17, 1998.
See also the extensive list of references contained
therein.
[FIS98] M. Fisher, C. Cumming, M. la Grone, R. Taylor, "An Electrostatic Particle Sampler and Chemical Sensor System for Landmine Detection by Chemical Signature", in SPIE Proc. Vol. 3392, pp. 565-574, Orlando, FLA, April 13-17, 1998.
[GEH99] M. Gehrke, S. Kapila, V. Flanigan, "Development of a Fast and Efficient Sample Enrichment Device for Semivolatile Organics", in SPIE Proc. Vol. 3710, pp. 433-444, Orlando, FLA, April 5-9, 1999.
[GEI99] M. W. Geis, R. R. Kunz, "Chemical Concentrator for Rapid Vapor Detection", in SPIE Proc. Vol. 3710, pp. 421-432, Orlando, FLA, April 5-9, 1999.
[GEO99] V. George, T. F. Jenkins, D. C. Leggett, J. H. Cragin, J. Phelan, J. Oxley, J. Pennington, "Progress on Determining the Vapor Signature of a Buried Landmine", in SPIE Proc. Vol. 3710, pp. 258-269, Orlando, FLA, April 5-9, 1999.
[HOR98] C. Horwood, B. Howell, R. Keeley, J.-B. Richardier (Eds.), "The use of dogs for operations related to humanitarian mine clearance", (2nd quarter of) 1998, ISBN 2-909064-33-6, 229 pp. Presented at the 2nd International Expert Conf. on the Use of Modern Demining Technology at Karlsruhe (Germany), 1 July 1998.
[LJU99] (Proceedings of the) World-Wide Mine
Detecting
Dog Workshop, Ljubljana, Slovenia, Sept. 13-15, 1999.
Available from HDIC at the James Madison University (http://www.hdic.jmu.edu/,
E-mail hdic@jmu.edu).
[PHE98] J. M. Phelan, S. W. Webb, "Simulation of the Environmental Fate and Transport of Chemical Signatures from Buried Landmines", in SPIE Proc. Vol. 3392, pp. 509-520, Orlando, FLA, April 13-17, 1998.
[ROD00] P. J. Rodacy, P. K. Walker, S. D. Reber, J. Phelan, J. V. Andre, "Explosive Detection in the Marine Environment and on Land Using Ion Mobility Spectroscopy: A Summary of Field Tests", Sandia Report SAND2000-0921, Sandia National Laboratories, Albuquerque, NM, April 2000, 20 pp. (Unclassified).
[WEB99] S. W. Webb, K, Pruess, J. M. Phelan, S. A. Finsterle, "Development of a Mechanistic Model for the Movement of Chemical Signatures From Buried Landmines/UXO", in SPIE Proc. Vol. 3710, pp. 270-282, Orlando, FLA, April 5-9, 1999.
SWITZERLAND
OTHER
Institut fuer Rechtsmedizin, Univ. Bern (Forensic
Medicine
Institute)
Geneva International Centre for Humanitarian Demining
(GICHD)
Police Cantonale Vaudoise, Groupement Specialistes
Depiegeage
(Canton of Vaud Police)
ARMY, Defence (General)
Current applications of neutron backscatter systems include for example the discrimination of ordnance containing explosives, inert substances and chemical warfare agents based on the considerable differences in their hydrogen content. A system has also been reported to have been in use for quite some time to detect explosives hidden in car doors, tyres, etc. For the detection of buried objects (e.g. landmines) the system has problems in presence of too much water and seems therefore likely to only work in dry or slightly humid environments. Tests with a time-tagged radioactive source are detailed in [CRA00] (for landmine detection).
The "Neutrotest" system developed by I.U.T. (http://www.iut-berlin.de/), for example, is composed from a technical point view of a BF3 proportional neutron counter and a fast neutron radioactive source, usually of the AmBe (Americium-Beryllium) type, located in the same head. The final system is rather light and simple, and gives a quick answer useful to prescreen objects. Known calibration curves are used, or scaling factors when encountering new geometries. In the case of larger munition several measurements might have to be taken along its profile.
HCM (Hydrogen Concentration Monitor), developed by the German Armed Forces Scientific Institute for Protection Technologies - NBC-Protection (WIS-ABC) in Munster, Germany, uses a small and weak 252Cf source and a 3He thermal neutron detector [BUC98]. The dimensions of the sensor system are 50x60x200 mm with a weight of 1.2 kg. As some background is generated in the floor and the walls of a building, a certain distance from the floor, depending on the object being analysed, is necessary. A counting time of 60 sec is sufficient to accumulate about 1000 events (i.e. backscattered neutrons), which results in a statistical uncertainty of 3%. The counting rate is influenced by the diameter of the samples (shells), the wall thickness and material. Standard calibration curves have therefore to be measured for different shell calibres and wall materials, and correction factors for pallets for example. A database containing the detailed calibration curves is integrated into the HCM evaluation software. The HCM is in use by the OPCW (Organisation for the Prohibition of Chemical Weapons) inspectors.
HCM is sold in Germany by ESM Eberline Instruments GmbH, Frauenauracher Str. 96, D-91056 Erlangen, Germany, Tel. +49 (0)9131-909-0, Fax +49 (0)9131-909-205. It is distributed in other parts of Europe by John Caunt Scientific Limited, PO Box 1052, Oxford OX2 6YE, UK (http://www.johncaunt.com/, John Caunt <johncaunt@dial.pipex.com>).
The application of neutron backscatter systems for
the
task of interest to us is likely to be problematic: 1) for partially
buried munition (soil influence), 2) for unknown munition
(unknown
calibration curve), 3) and possibly also when detecting black powder
(does not contain hydrogen, see §1.1) or incendiary munition
(does usually not contain hydrogen). Hydrogen will be present in some
inert
fillers such as waxes, or whenever some water is present, which might
increase
the false alarm rate. On the other hand it might still be true that
when
no signal is detected no hydrogen - and therefore no explosive - is
contained
in the UXO. Whether this turns out to be useful in practice remains
to be seen, but the simplicity of neutron backscatter devices might
well
warrant some practical investigation. Obviously only if it is
possible
to put the detector in contact with the UXO, or at least in close
proximity.
An example of such a sensor is the SEARCHER unit, which is already in use for police and customs applications. The unit is battery powered and one-man portable, and relies on a cobalt-57 (57Co) source and associated detector electronics to detect the presence of material within a depth of about 10 cm. A simple audible signal is delivered, which also depends on the thickness of the material being analysed; with use the operator learns to interpret the audible signals. The source has a half-life of 270 days, therefore a source change is recommended every two years (although adjusting the gain allows to reach four years). Note that when the probe is turned ON and in use, no part of any person should be allowed within 30 cm of the face of the probe. The approximate price is in the 10.000£ range.
The SEARCHER was developed by JCS (John Caunt Scientific Limited, coordinates as in §A1.1), and is sold through S&D Security (Equipment) Ltd.
The SAIC CDS-2002i™ Contraband
Detector
is probably another unit working on similar principles. It employs a
low-level
100 mCi (Standard) or a 10mCi
(Exempt) 133Ba radioactive source, and is detailed at http://www.saic.com/products/security/contraband_detector/cds.html.
One of them is CDS (Chlorine Detection System) by the German Armed Forces Scientific Institute for Protection Technologies - NBC-Protection (WIS-ABC) in Munster, Germany, which was presented to the OPCW (Organisation for the Prohibition of Chemical Weapons) in Sept. 1997 partly as an alternative to the more comprehensive but larger NIPPS system (see §3.4). CDS is a small and rugged device relying on a 252Cf source (10 times less intense than for the normal NIPPS system) and on a compact uncooled BGO detector to detect the chlorine capture g-rays (the most intense have an energy of 1.165, 1.955 and 6.111 MeV). Chlorine concentrations above 20 g can be measured in 2 to 5 minutes [BUC97].
CDS is sold in Germany by Target Systemelectronic GmbH, Kölner Str. 99, D-42651 Solingen, Germany, Tel. +49 (0)212-2220-9090, Fax +49 (0)212-201045.
A particular form of NMR, the Fourier Transform Proton (i.e. Hydrogen) NMR (FT-1H-NMR), has been suggested for the detection of explosives. By analysing and processing the total hydrogen NMR signal, any contribution to the response produced by hydrogen in explosives can be separated from that (usually much larger) produced by the hydrogen in most other materials. In practical terms, the RF field is applied in short pulses of controlled width and amplitude, and the corresponding NMR responses are transient RF signals emitted by the excited nuclei. Two parameters have a particular importance, T1 and T2. T1 is the so-called spin-lattice relaxation time, which is the characteristic time for a nuclear spin system to come to equilibrium with its surroundings after a disturbance (such as the previously mentioned RF pulses, or a change in the applied field). T1 sets the time required to detect an NMR response, and the rate at which NMR tests might be repeated without signal degradation. T2 is the so-called spin-spin relaxation time, which is the characteristic time for a spin system to come to transversal equilibrium following a disturbance. The transient, free induction decay (FID) signal following a single transmitter pulse decreases in amplitude at a rate which is dependent upon T2 (in a homogenous magnetic field).
T1 and T2 are characteristic of the molecular structure and the state of the sample material. Measurements have been reported, in particular at a frequency of 3 MHz, showing that these two constants for explosives can be well separated from other common materials of interest, T1 being long (1-10 sec) and T2 short (10-4-10-6 sec). Additional selectivity is provided in FT-1H-NMR by the 1H-NMR to 14N-NQR level crossings, but we will not go here into further details. Note that the sensitivity is not affected by the distribution of the sample, only by the total material present.
NMR techniques can therefore determine the presence of materials with the chemical composition of explosives. The FT-1H-NMR technique described above has been in particular extensively tested. All samples, however, must be passed through the magnetic coils (with a higher field intensity allowing higher signal to noise ratios), thus limiting accessibility and configuration of NMR systems. This is probably one of the reasons why no such systems are commercially available, to the best of our knowledge. Other reasons might be the detection time, or the need for very good field homogeneity over large working volumes. The inability of detecting explosive contained within metallic enclosures (screening by Faraday effect) might also be a problem (see also the NQR section). Iron or large amounts of ferromagnetic metals can cause field distortion and reduce effectiveness.
NMR techniques for the detection of explosives have been for example extensively studied at the South West Research Institute (http://www.swri.org/). See for example "Baggage Inspection Apparatus and Method for Determining Presences of Explosives", A. De Los Santos, J. D. King, W. L. Rollwitz, G. A. Matzkanin, P. A. Hornung, South West Research Institute, US Patent # 4,514,691, 30/04/1985, and also [YIN93a]. NMR techniques for drug detection have also been studied at Quantum Magnetics (http://www.qm.com/).
We will not enter here into the details of another RF resonance absorption method, Electron Spin Resonance (ESR) or Electron Paramagnetic Resonance (EPR), just mentioning that it is limited to small proportion of materials (those which have free spins), but when applicable is much more sensitive than NMR. One such material is black powder, which cannot be detected by proton NMR (it does not contain hydrogen).
Unlike NMR where an external (static) magnetic field is needed, quadrupole resonance takes advantage of the material's natural crystalline electric field gradient, i.e. the electrical gradients available within the molecule itself. These gradients are due to the distribution of the electrical charge within the molecule and do therefore depend on the chemical structure (they will be different for RDX, for TNT, etc.). The electrical field gradients align the electric quadrupole moments, which are a physical property due to a non-spherical (say ellipsoidal) nuclear charge distribution, of the 14N nuclei. As a result, the material being diagnosed need not be contained within large magnetic field-producing coils. NQR resembles therefore to NMR without a magnet.
When a low-intensity RF signal is applied to the material at certain frequencies, usually in the range 0.5 to 6 MHz, the alignment of the 14N nuclei is altered. As the RF is removed, the nuclei precess to their original state (actually a transition between the energy states resulting from the previously described interaction), producing a characteristic radio signal. The signal can then be measured for analysis. Detecting the presence of explosives becomes similar to tuning a radio to a particular station, and the uniqueness of a molecule's electric field allows NQR technology to be highly compound specific. This high selectivity is partly a disadvantage, as it is apparently not that easy to build a multichannel system necessary to cover a wide range of target substances.
The actual setup (geometry) depends on the application at hand, and there are a number of situations, such as in landmine detection and perhaps for the identification of IEDs, in which a single-sided (remote) geometry is necessary, as it might be impossible to put parts of the sensor on "the other side of the object". Also, similarly to metal detectors the generated and the received field decay very quickly with distance; the detection distance will therefore be limited and the equipment will probably have to be used in close proximity to the object or to the ground. Power requirements are also considerable. Whether these issues are problematic depends obviously a lot from the target application.
The impossibility of detecting substances fully screened by metallic enclosures (also foils, depending on their thickness) is an issue like for NMR. What will however probably happen is that the presence of such objects throws the NQR probe out of tune, in which case the operator knows that something is wrong. It might also still be possible to detect explosives in imperfectly shielded objects, e.g. within metallic containers having holes or slots or other regions where there are poor electrical connections (possibly even some UXO!), but this will result in a correspondingly weaker NQR signal. Practical applicability is therefore likely to be an issue.
Detection times are likely to be higher than a few (tens of) seconds, depending on type and quantity of the target substance (especially on its T1 relaxation time), and on its distance for one-sided applications. In addition, the signal to noise ratio increases with frequency as w3/2, which implies that detection of TNT is much harder than detection of RDX, for which NQR systems have been shown to be very promising. Signals are in general rather weak, so that some form of signal averaging is usually necessary - as well as shielding, because the detector will work (at least for TNT) straight in the AM broadcasting band! Spurious signals have also been reported due to "acoustic ringing" effects (due to certain metals and metal coatings), as well as due to piezoelectric responses from silica in the soil (for applications such as landmine detection). All these effect are being tackled using appropriate pulsing sequences and detection software, as well as specific hardware. Care will have also to be taken of the temperature dependency of the spectral lines, selecting for example those NQR transitions which are least affected by temperature changes (e.g. 3.410 MHz line instead of 5.192 MHz for RDX).
NQR for explosive detection has been intensively researched in both the UK and US in the context of defence applications, in particular in the UK at King's College in London (KCL, Prof. John Smith) under sponsorship of DERA, at DERA itself and at ERA Technology (especially equipment manufacturing, http://www.era.co.uk/, David.Daniels@era.co.uk) [BRU99]. In the US Quantum Magnetics, now part of InVision Technologies, has licensed the NQR technique from the Naval Research Lab and is also currently engaged in prototype developments (http://www.qm.com/). At the time of writing there are actually two systems being advertised by Quantum Magnetics, the QSAN™ QR160 (for carry-on baggage) and the QSAN™ QR 500 (for checked baggage, mail and parcels); these detectors are two channel systems. Some prices are quoted in [NIJ98]. R&D was also carried out in the former Soviet Union, in Kaliningrad (Prof. Grechiskin, Kaliningrad State University) and in Novosibirsk, as well as in Slovenia (R. Blinc, Jozef Stefan Institute, Ljubljana). Note that some of the work has also been aimed at the analysis of suspicious objects using different system configurations, but no commercially available systems have appeared yet (equipment is only available to a bespoke design requirement).
A few key points will be summarised in the following paragraphs, which do not pretend to be exhaustive, also because individual techniques often vary considerably according to the precise circumstances and much can be left to individual judgement. In addition, the case of Improvised Explosive Devices (IEDs) presents understandable security issues.
Operational aspects and scenarios pertaining to Law Enforcement applications are considered in detail in [NIJ99a, NIJ98], as well as in [NAV97].
Still concerning X-ray systems, INEEL (Idaho National Engineering and Environmental Laboratory) has developed a field portable X-ray Digital Radiography and Computed Tomography (DRCT) scanner, which has allowed to obtain high-quality radiographs and tomographic images of (chemical) munition at the site where the munition is stored or recovered [RON00]. Stereoscopic methods have also been suggested to provide information about the depth structure of the object being analysed [RAN99]. Fixed site tomographic installations for Non-Destructive Ordnance Evaluation have also been reported, but these are probably large systems and do not directly concern EOD applications.
Last but absolutely not least, whether or not the probing method or system being investigated risks to activate the UXO's detonator, either because of the probing radiation itself or because of the system's electronics for example, should obviously be known or checked beforehand (!).
To analyse the object's state and internals portable X-ray equipment is used by some units, again combined with radiographic films or real-time imaging systems (most of the comments of A2.1 still apply).
Concerning bulk explosive detection, neutron backscatter devices, which are basically hydrogen detectors, have apparently also been employed (see A1.1). Thermal Neutron Analysis (TNA) systems have been tested for airport security applications (see also A2.3). They seem to be commercially available in different versions, e.g. from the ANCORE Corp., to check mail, parcels, cars, etc., mostly as fixed installations. Their actual level of diffusion is not clear. Whether neutron based systems will get really portable remains to be seen. Radiation hazard is obviously also present and has to be dealt with. For a description of advanced X-ray systems see again §2.1, and §A2.3.
Work is ongoing on Nuclear Quadrupole Resonance (NQR) based systems (see A1.5), for example either by using a single coil in a one sided geometry, or by employing pairs of coils when the object can be accessed from both sides. Nuclear Magnetic Resonance (NMR, see A1.4) was also seen as a potential candidate in the late 80's, early 90's.
Trace explosive detection devices are on the other hand widely available, although opinions diverge on their practical applicability for this task. One of the key issues resides in how to bring the explosive (in)to the probe and how to maximise the sampling efficiency, see for example §4.1 and Annex A3 as well as the references cited therein.
New bulk explosive detection techniques seem to have been tested in the last years, for example NQR or TNA, but apparently it is not easy to satisfy all the requirements, in particular the need for high throughput (and therefore little time for each piece of luggage, say some seconds) coupled to a reasonably low false alarm rate. A reasonable cost and complexity do also play a role, as well as environmental factors for example in the case of neutron based systems. An additional complexity comes from the need of having to detect a relatively small device in a large complex and variable matrix (a piece of luggage and its contents). As an example, problems with TNA systems due to the presence of other nitrogen containing substances (including food!) have been reported. On the other hand, the dissuasive role of explosive detection equipment should probably not be underestimated.
Trace explosive detection has seen an increasing level of success in the last couple of decades, is now routinely featured in a number of airports and seems to feature a rather low false alarm rate. Particle detection in particular is feasible, as the objects at hand can be touched and swiped. To have an idea of which trace explosive detection systems are deployed see for example [NAP99, Ch. 7] for the case of US airports.
We will not enter here into further details, nor cover other applications such as the detection of explosives in large containers.
As in [NIJ99a], inclusion of specific technologies in this document does not represent endorsement of the corresponding systems. Also, these references do not pretend to be all-inclusive.
The ions are then periodically admitted into the drift region through an electronically shuttered gate. This "drift" of the ions from one end of the drift region to the other occurs at atmospheric pressure, with many collisions between the ions and the various molecules present. The time it takes the ions to travel the length of the drift region is called the drift time and depends on their mobility. The drift time is a complex function of the charge, mass, and size of the ion (and its molecular structure?), and allows the identification of the substance. Typical drift times are on the order of a few milliseconds (1 ms = 0.001 s). Examples of ion mobility spectra are shown in [YIN99] as well as in several of the manufacturers' brochures.
The current collected at the metal plate is measured as a function of time, and an IMS spectrum is a plot of ion current versus time, with different peaks representing different specific ions. Sometimes an additional gas called the dopant or carrier gas is admitted into the IMS to aid in the ionisation process; very commonly methylene chloride or some other gas that easily forms chloride ions is used. Ions from this gas usually form the largest peak in the IMS spectrum, commonly known as the reactant ion peak or RIP, which serves as a reference peak. The overall signal to noise ratio is usually increased by repetitively scanning the spectrum and signal averaging (a single mobility spectrum can be generated in some tens of msec).
A number of companies market IMS systems, see
Table 6.
Upkeep costs vary from system to system, but are moderate in most
cases.
Most IMS systems are small and portable enough to be moved around in a
standard vehicle, and can be operated by a person with only a few hours
of training. These instruments have response times of only a few
seconds,
the proven ability to detect a number of key explosives,
sub-ppb/sub-nanogram
sensitivity and low false alarm rate. The most effective means for
collecting
a sample for presentation to one of these systems is surface swiping,
but
vacuum collection of samples is also possible with many systems. Some
of
the potential drawbacks include:
Explosive molecule ® (pyrolysis) n NO + k NO2 + ..., NO + O3® NO2* + O2 , NO2* ® NO2+ hn (IR)
Chemiluminescence by itself is not capable of identifying what type of explosive molecule is present, as the NO could have been produced by other substances (i.e. interferents). CL detectors are therefore coupled to a front-end gas chromatograph (GC), which allows different molecules that are detected with the chemiluminescence detector to be specifically identified based on their GC retention times. An example of such a GC/CL detector is the Thermedics EGIS, which is capable of analysing samples in 18 seconds. Because of its high sensitivity and excellent selectivity it is a popular system with laboratory researchers and forensic analysts [NIJ99a] (although 2 to 3 times more expensive than typical IMS systems).
The basic principle behind an ECD is that this standing current is characteristic of the gas mixture being drawn into the system. Actually, it is reduced if the vapour of an explosive enters the chamber because the explosive molecules have a high electron affinity and thus a tendency to capture free electrons and form stable negative ions, leaving fewer electrons to reach the anode. As with a chemiluminescence detector, a gas chromatograph is placed on the front end of an ECD system to allow temporal identification of different explosives. For additional information see also [NAV97].
GC/ECD detectors have a rapid response and typical sensitivities of about 1 ppb for most electron-capturing compounds (somewhat less than a typical IMS or CL system, but is still adequate for some applications). At this point we would in fact have to differentiate better between laboratory and field based instruments.
GC/ECD (field?) detectors tend to cost less than
IMS or
CL, and to be smaller, lighter, and more easily portable. Some of the
drawbacks
include:
SAW sensors are for example marketed by Electronic Sensor Technology, Inc.. Total analysis time, including sample concentration in the cryo-trap, is typically 10 s to 15 s. The system is advertised to have ppb sensitivity to certain types of explosives, is about the size of a large briefcase, and is operational within 10 min of startup [NIJ99a]. [NIJ98, p. 13] and [YIN99] quote a sensitivity to picogram levels of explosives.
The TR system currently marketed by Intelligent Detection Systems (formerly Scintrex), the EVD-3000, is a hand-held unit which can analyse both vapour and particle samples. Since only the presence of NO2 groups is detected, this technology cannot distinguish among different explosives and potential interferents that contain NO2 groups.
The sole manufacturer of FIS sensors seems to be Mine Safety Applications (MSA). The sensor has no moving parts except for a small recirculation fan and no consumables except for a replaceable calibrator and gas purification filters. The manufacturer has reported detection limits for some high explosives in the low picogram range, as well as a response time of 2 s for a single target molecule plus another 5 s for each additional target molecule (the device can be tuned so that only specific ions, those of interest, can pass completely through the analytical volume and into the collection area for detection).
Because of the newness of this technique, the current systems may be better adapted to laboratory research than to routine field applications, but this could change in the future. The system's maturity is not clear from the corresponding Website.
Mass spectrometers have excellent specificity for identifying different ions, and some (field?) systems have sub-picogram sensitivity. SCIEX (Toronto, Canada) used for example to build a tandem mass spectrometer coupled to an ionisation source operating at atmospheric pressure (API-MS/MS) which was very sensitive (vapour: a few ppt; particle: picogram amount) and fast. Even lower sensitivities are achievable, e.g. 10 fg TNT for a API-TOF MS system quoted in [YIN99, §2.5.2.3]. Syagen (http://www.syagen.com/) has developed a QitTof™ (quadrupole ion trap, time-of-flight) mass analyser that is apparently also quite sensitive.
Several portable systems have been advertised in the last years according to [NIJ98], but not necessarily designed specifically for explosive detection. An example is the Inficon HAPSITE field portable GC/MS (http://www.hapsite.com/) (weight: 16 kg, batteries included), designed for on-site analysis of volatile organic hazardous air pollutants (VOHAPs) in air, soil and water, for emergency response and environmental applications.
The USE is coded as follows: PER/PCK/VEH: Personnel, Package and Vehicle search; PORTAL: Personnel portal (fixed checkpoint portal); POR/LAB: Portable analytical laboratory instrument; NARC/EXPL: simultaneous narcotics and explosives. Detector Type: Vap stands for vapour detector, Part for Particle detector. Advertised Sensitivity/Detection Time: A stands for Analysis time, S for Sampling time.
| Trace Detector | Cost
in k$ |
Detector
Type |
Advertised
Sensitivity/ Detection Time |
Use | Size
/ Weight |
| EXPRAY
Field
Test Kit Model M1553 |
0.25 | Colour | 20 ng of most nitrated high explosives | PER/PCK/VEH | 3
aerosol cans, 1 lb. |
| Ion
Track Instruments Exfinder 152 |
5 | GC/ECD
Vap |
Most
nitrated
high Explosives A: 1 sec* |
PER/PCK/VEH | 2"x2"x16"
1.5 lb. |
| JGW
International,
Ltd. Graseby GVD4 |
5 | GC/ECD
Vap |
Explosive
vapour Exceeding 1 part in 109 |
PER/PCK/VEH | 2"x3"x13" 1.6 lb. |
| XID
Corporation XID Model T-54 |
13 | GC/ECD | 0.01 ppb | PER/PCK/VEH | 4"x12"x17" 18 lb. |
| JGW
International,
Ltd. Graseby GVD6 |
16 | IMS
Vap |
Explosive
vapour
exceeding 1 part in 109 (1 part in 1010 by volume*) |
PER/PCK/VEH | 22"x4"x13" 21 lb. |
| Ion
Track Instruments Model 97 |
20 | GC/ECD
Vap (+Part.) |
Most
nitrated
high Explosives A: 3 sec* |
PER/PCK/VEH | 14"x19"x6"
40 lb. |
| Scintrex/IDS
EVD-3000 |
23 | TR
Vap+Part |
<
1 ppb
(< 50 ppt for EGDN?) < 100 nanogram for Part. A: 10 sec, S: 5-30 sec |
PER/PCK/VEH | 4"x5"x20"
7 lb. |
| Electronic
Sensor Tech., Inc. EST Model 4100 |
25 | GC/SAW
Vap? |
100
ppb? (low
ppb*) A(Total): 10-15 sec |
PER/PCK/VEH | 10"x20"x14"
35 lb. |
| MSA
Instrument
Division FIS |
29 | FIS | 10 to 1000 ppt | PER/PCK/VEH | 24"x15"x13"
20 lb. |
| Ion
Track Instruments ITMS Vapour Tracer |
38 | IMS
(ITMS) Vap |
100
to 300
pg (10 to 50 pg*) A+S(?): 4-10 sec* |
PER/PCK/VEH | 13"x5"x5"
7 lb. |
| Ion
Track Instruments ITEMISER |
44 | IMS
(ITMS) Part? |
100
to 300
pg (<30 pg*) A: 3-8 sec |
PER/PCK/VEH | 18"x21"x14"
43 lb. |
| Ion
Track Instruments Model 85 Entry Scan |
52 | GC/ECD | 1
part EGDN
vapour in 1011 parts air |
PORTAL | 80"x33"x60"
600 lb. |
| Ion
Track Instruments Model 85 Dual Scan |
52 | GC/ECD | 1
part EGDN
vapour in 1011 parts air |
PORTAL | 80"x33"x60"
600 lb. |
| Barringer
Instruments, Inc. IONSCAN 400 |
60 | IMS
Part |
50-200
pg A: 5-8 sec |
PER/PCK/VEH | 22"x13"x12"
60 lb. |
| Intelligent
Detection Systems ORION |
70 | GC/IMS
Vap+Part? |
pg
to ng for
particulates ppt for vapours. A: 6 sec |
PER/PCK/VEH | 40"x20"x30"
240 lb. |
| VIKING
Instruments,
Inc. Spectra Trak |
70 | GC/MS | Low
ppb By volume |
POR/
LAB |
24"x16"x21"
150 lb. |
| Intelligent
Detection Systems ORION Mail Scanner |
75 | GC/IMS | pg to ng | MAIL
screening |
40"x20"x30"
240 lb. |
| Intelligent
Detection Systems SIRIUS |
75 | GC/IMS | pg to ng | NARC/
EXPL |
40"x20"x30"
240 lb. |
| Thermedics
Detection, Inc. EGIS Model 3000 |
150 | GC/CL
Vap+Part |
All
nitrogen
based Explosives plus taggants A: 18 sec, S:? (10-20 sec?) |
PER/PCK/VEH | 51"x25"x26"
400 lb. |
| Intelligent
Detection Systems ORION Plus |
155 | GC/IMS | pg to ng | PER/PCK/VEH | 40"x20"x30"
240 lb. |
Table 6: Commercially available Trace explosives detection systems (adapted from [NIJ99a], Table 4; *: info from the manufacturers' brochures and/or [NAV00]; 1 lb=1 pound=0.454 kg, 1"=1 inch=2.54 cm)
The following systems represent an addition to those listed in the original [NIJ99a] table, most of them having been marketed since:
GC-IONSCAN: GC-IMS, "fully transportable field screening instrument" (manufacturer's notice), weight 32 kg, dim. 41x53x45 cm, analysis time < 5 min (one minute example shown for explosives).
SABRE 2000: IMS, weight 2.6 kg, dim. 33x11.5x13cm, detection limit for most substances: low ng range. Vap+Part, A: 10-15 sec.
Sensitivity: 0.01 ppb for
TNT (10-13g
/cm3 = 0.1 pg/cm3), weight 1.3 kg (hand held
unit),
dim. 9x10x31 cm, A+S: 2 sec [RAN99]. Marketed as EXPLORER 2000 in the
US.
Send questions, comments or corrections to
.