NOTE
In cases where the supporting laboratory cannot be contacted, as a minimum the following specimens should be collected: Urine—25 to 50 ml in a sterile container. Blood—two 7 to 10 ml tubes without anticoagulant (red-stopper VacutainerTM); two 7 to 10 ml tubes with potassium or sodium ethylenediaminetetraacetate (EDTA) (lavender-stopper VacutainerTM).
b. Post mortem and Forensic Specimens. The analysis of specimens from deceased humans and animals can provide valuable information about the disease, organisms, injuries, or environmental conditions at the time of death. This information can greatly enhance the treatment of others affected by the same, or physiologically similar, process. Specimen collection for post mortem or forensic examination is very important; the techniques involved reflect a significant degree of training, experience, and skill. Most specimens will be of the same type and size as for ante mortem specimens, but types and amounts of specimens will be determined by the collector.
(1) The collection of specimens from remains should be conducted exclusively by a pathologist, or other personnel specifically trained in forensic collection techniques. An exception is when Special Operations Forces (SOF) personnel are operating under radio silence conditions; the most qualified medical person with the operation collects, preserves, and transports or coordinates transport of specimens for evaluation. The same chain of custody requirements applies to specimens collected by SOF personnel, as with all other specimens.
(2) A large amount of support information can be gained by analyzing the site of injury and subsequent death. This "site scene" investigation requires a tremendous attention to detail and a trained observer. If forensic personnel cannot be contacted, or will be unduly delayed in arriving at the scene, then photographs of the victim and the immediate surroundings should be made. The scope and extent of the photographs should be composed to reflect as much detail as possible to assist forensic personnel in reviewing the scene retrospectively. In the event that photography is not feasible, detailed sketches of the scene should be made to assist the forensic investigation.
(3) Techniques such as cardiac or bladder puncture, needle biopsy of organs, spinal tap, or exploratory laparotomy will not be performed by untrained personnel unless specifically requested and directed by forensic investigators.
Table B-1. Specimen Collection for Suspect Biological Warfare Agents
| BC | Blood culture |
| C | Citrated blood |
| CSF | cerebrospinal fluid |
| DNA | deoxyribonucleic acid |
| E | EDTA |
| EEE | eastern equine encephalitis |
| ELISA | enzyme-linked immunosorbent assay |
| EM | electron microscopy |
| F-1 | fraction-1 |
| FA | fluorescent antibody |
| H | Heparin |
| HPLC | high-pressure liquid chromatography |
| IgG | immunoglobulin class G |
| IgM | immunoglobulin class M |
| PCR | polymerase chain reaction |
| RT | Red Top, if TT is not available |
| RT-PCR | reverse transcriptase/ polymerase chain reaction |
| TT | Tiger top |
| VEE | Venezuelan equine encephalitis |
| WEE | western equine encephalitis |
c. Water Sample Collection.
(1) Water samples for identification or verification of biological agent contamination are collected by PVNTMED personnel. The supporting laboratory should provide guidance on sampling procedures and collecting kits for use in collecting the samples. In the absence of guidance, a technique for use of the Sep-PakTM is described in FM 3-19.
(2) When sampling kits are not available, samples may be collected in other available sterile containers. The best containers for use are the 100-ml glass bottles used for collecting routine water samples. All water samples must be collected and placed in a cooler or refrigerator until the sample is transported to its destination. During transportation the samples must be maintained at a temperature between 1°C and 4°C.
d. Food Samples. Veterinary personnel must collect suspect biologically contaminated food samples for submission to the supporting laboratory for in-theater verification of contamination. All food samples must be collected and placed in sterile containers. Place the samples in a cooler or refrigerator until the sample is transported to its destination. During transportation the samples must be maintained at a temperature between 1°C and 4°C.
e. Animal Specimens. Veterinary personnel collect specimens from suspect biologically contaminated/diseased animals. The same types and amounts of specimens are prepared and shipped in the same manner as are human specimens.
f. Environmental Samples. Environmental samples are collected as directed in the operators' manual or other publications for operating collection systems. Example: The Biological Integrated Detection System (BIDS) collects an environmental sample using a single liquid sample collector. The collector is a high-volume aerosol sampling and collection device. On demand it samples ambient air through a two-stage virtual impactor that concentrates aerosol particles in the 2 to 10 micrometer diameter-size range. The concentrate particle stream is directed through a wet collector containing a buffer solution and, over a 45-minute period, a 40 to 50 ml sample is collected. On order or when test results indicate a suspected agent, the sample and associated documentation are packaged and transported IAW FM 3-101-4.
a. A strict chain of custody must be maintained for every sample/specimen collected. Use DD Form 1911 (Material Courier Receipt), or other document (such as DA Form 4137 [Evidence/Property Custody Document]) as directed for each sample/specimen collected. The chain of custody document must accompany the sample/specimen during transport from the point of collection to the final receiving laboratory. Each time the sample/specimen is transferred to another individual, the receiving person must sign the document to show that they received the sample/specimen and state what happened to the sample/specimen while in their custody. The document will provide the answer to the following questions:
b. The samples/specimens must be appropriately packaged, labeled, and evacuated to the designated medical laboratory for confirmation of a biological attack. The standard chain of custody for the evacuation would be as follows:
The collection of environmental, and background (control) samples/medical specimens is an integral part of investigating allegations pertaining to the first use of chemical or biological agents. The types of samples/specimens taken and the collection methods primarily depend upon the circumstances encountered by the collector. During all chemical and biological sampling operations, the commander establishes the required protective equipment to fit the situation. This appendix includes a recommended list of equipment for use during chemical and biological sampling operations (Table B-2).
Table B-2. Example NBC Collection and Shipping Equipment List
| AMOUNT | DESCRIPTION | STOCK NUMBER | |
|---|---|---|---|
| 20 | LABELS, PAPER, PRESSURE SENSITIVE | 7530-00-577-4376 | |
| 2 | GLOVES, 8-8½, EDMONT WILSONTM | 8415-00-JO2-2902 | |
| 2 | GLOVES, 9-9½, EDMONT WILSONTM | 8415-00-634-4639 | |
| 1 | TAPE, ADHESIVE, PRESSURE SENSITIVE, 2 INCH | 7510-00-159-4450 | |
| 1 | PLIERS, #47, 5 INCHES | 6520-00-543-5330 | |
| 1 | SCREWDRIVER, FLAT TIP, ¼ INCH | 5120-00-596-865 | |
| 1 | TONGS, TEFLONTM TIPS | AF 15-202-5 | |
| 2 | MICROSPATULA, WITH TEFLONTM ENDS | AF 21-401-50A | |
| 1 | SCISSORS, UNIVERSAL TYPE | AF 08-951-30 | |
| 1 | SCOOP, POLYPROPYLENE, 5X2X2 | ASP S1021-5 | |
| 2 | SPOON/SPATULA WITH TEFLONTM | AF 14-356-10 | |
| 1 | KNIFE, POCKET | 5110-00-526-8740 | |
| 5 | BOTTLES, SAMPLE, POLYETHYLENE, 6 OUNCE | CP J-6103-50 | |
| 1 | PIPET, JUMBO, TRANSFER TYPE (500/PKG) | AF 13-711-7 | |
| 10 | PIPET, GRADUAL, TRANSFER TYPE (500/PKG) | AF 13-711-9A | |
| 10 | BAG, INSULATED, TYPE I | AF 01-814-8 | |
| 10 | BAG, INSULATED, TYPE 2[*] | AF 01-814-10 | |
| 1 | BAG, WHIRL/PAK, 6 OUNCE (500/PKG) | AF 01-812-6B | |
| 1 | STRIP, pH TESTING, NONBLEEDING, PLASTIC | SW S-65271 | |
| 1 | SEP-PAKTM C18 | W51910 (50/BOX) | |
| 2 | SYRINGE, HYPODERMIC, 50 OR 60 ml | 6515-00-168-6913 | |
| 2 | STOPCOCK, THREE-WAY | ASP S8965-2 | |
| 1 | TUBING, LABORATORY, R3602 CLEAR | AF 14-169-3B | |
| 1 | PEN, MARKING, WATERPROOF | AF13-381 (12/PKG) | |
| 2 | TUBES, TENAXTM | EC ST-023 | |
| 1 | BLADE, SURGICAL, CS2L 150S | 6515-01-009-5297 | |
| 2 | PACK, ICE | CP TR-6345-20 | |
| 6 | PAD, NONADHESIVE, 3X4, 100s | 6510-00-111-0708 | |
| 4 | PAD, COOLING, CHEMICAL, 4S | 6530-00-133-4299 | |
| 2 | PIGLETTES | SPECIAL ORDER | |
| 1 | TAPE, ANTISEIZE | 8030-00-889-3535 | |
| 1 | AIR SAMPLER, PERSONAL | LSS G4980 | |
| 1 | KIT, METRIC, POCKET BUBBLE | GL4981 | |
| 2 | METHANOL | ||
| 1 | WATER, DISTILLED (5 BOTTLE/PKG) | ||
| 1 | MATCHES, WATERPROOF | ||
| 20 | RAZOR, SURGICAL PREP | 6515-00-926-2089 | |
| 10 | WATCH, WRIST | 6645-00-066-4279 | |
| 2 | PARAFILM WITH DISPENSER | 6640-01-185-3289 | |
| 2 | FLOOR SWEEP (VERMICULITE) | 8720-01-026-9419 | |
| 100 | SEALS, TAMPER-RESISTANT | ||
| 1 | A GAS METER CAPABLE OF PROVIDING ON-STATION ANALYSIS/DETECTION CAPABILITY FOR MULTIPLE GASES TO INCLUDE INDUSTRIAL GASES. | ||
| 1 | A COMBUSTIBLE GAS INDICATOR THAT INDICATES PERCENTAGE OF OXYGEN AND EXPLOSIVITY. | ||
| 1 | A GAS METER THAT DETECTS VAPOR IN PARTS PER MILLION (PPM) AND INDICATES PRESENCE OF VAPOR AND ITS STRENGTH. | ||
| 1 | SWABS, THROAT | ||
| 2 | CAN, 6 POUND, METAL | ||
| 10 | BAG, MYLAR | ||
| 1 | CONTAINER, LEAD SHIELDING (FOR RADIATION SAMPLES) | ||
| 1 | CONTAINER, SHIPPING, IATA | ||
| 1 | CHEST, ICE | ||
| 10 | BAG, PLASTIC, RECLOSABLE | ||
| [*] WILL BE REPLACED BY MYLAR BAGS | |||
The NBC recon units collect samples under various circumstances. For example, a recon unit may collect samples in an area free of hostile forces. The Special Forces NBC Reconnaissance team may collect samples within the enemy area of operations or deep into the enemy's rear area. Samples include toxic agent munitions, chemical products, air, water, soil, and vegetation. In addition, all expended material used to collect the samples should be turned in to the laboratory with the samples. This material includes items such as expended M256A1 kits, M8 and M9 paper. These items should be recovered, packaged, and shipped with the suspected samples for analysis. Different information may be derived from each type of sample; Table B-3 compares different types of samples.
Control or background samples that are collected from clean samples must be identical to the samples collected from the areas near the attack areas as baseline data. The contaminated samples must be compared to the baseline data (control samples). This is especially true if unknown or nonstandard chemical and/or suspected biological agents were employed. The analysis center uses the control samples to compare with a contaminated one. The recon unit collects control samples of soil, water, and vegetation from areas about 500 meters upwind of an alleged attack area. Control samples generically are the same as those collected in an alleged attack area. For example, if leaves from an apple tree in an attack area were collected as a suspected contaminated sample, the recon team should collect leaves (as a control sample) from an apple tree outside of the contaminated area. If water from a pond in the attack area is collected, the recon unit should collect control samples of water from a pond (not a moving stream) in a nearby clean area. The size of an environmental control sample should be about the same as the suspected contaminated sample collected from the attack area (see Table B-4, page B-20).
Table B-3. Comparison of Sample Types
| SAMPLE STABILITY | ANALYSIS | |||
|---|---|---|---|---|
| SAMPLE TYPE | INFO VALUE | TO COLLECT | TIME REQUIRED | RELIABILITY |
| AIR | GOOD | GOOD | 20 MIN | HIGH |
| WATER | GOOD | GOOD | 5 MIN | HIGH |
| SOIL | FAIR | FAIR | 5 MIN | MODERATE |
| VEGETATION | FAIR | POOR | 10 MIN | LOW |
| TISSUE | EXCELLENT | FAIR | 30 MIN | HIGH |
| BLOOD | GOOD | FAIR | 10 MIN | HIGH |
| URINE | GOOD | FAIR | 10 MIN | HIGH |
| MUNITION FRAGMENTS | FAIR | FAIR | 10 MIN | FAIR |
| PACKING MATERIALS | FAIR | FAIR | 10 MIN | FAIR |
a. Air is a good sample matrix since it is a well-mixed medium. Air from a sample site contains a static concentration of contaminants. The concentration of contaminants depends upon the flow rate of the contaminant into the environment, the wind speed, and the physical state of the contaminant, the terrain contours, and temperature as a variable. The sample should be taken within 102 meters of a contaminated surface and at the downwind edge of a contaminated area. The method should consist of pumping a given volume of air, by hand or electric pump, through sample tubes.
b. To avoid contamination, persons conducting air sampling should not use cologne, perfume, insect repellent, medical creams, or strong soaps before taking a sample. The fragrances from these products are volatile organic compounds that may be absorbed on the filter and skew analytical results. Smoke also severely interferes with air sampling, therefore, avoid tobacco and vehicle exhaust smoke.
c. The primary method for collecting air samples is with the PAS 1000 automatic air sampler in conjunction with a TenaxTM tube for a total of three to four minutes when possible. Upon completion of sampling, place the TenaxTM tube in a 2¼-inch piglette. Seal the piglette around the cap with either pressure-sensitive or TeflonTM tape. Once sealed, place the piglette into a Mylar or reclosable bag. Fold the bag around the piglette in a circular motion, then apply another bag and fold again. Once the bag is folded around the piglette, use any type tape to secure the bag around the piglette. Place the piglette into a refrigerator or cooler until the sample is transported to its destination.
d. When chemicals are permitted into the atmosphere from a facility, the best places to obtain samples are close to the emission source where the concentration of the chemical is not diluted. The further from the original point of release, the more diluted the sample becomes from mixing with air, water, or environmental pollutants.
e. Natural and man-made terrain features such as hills, valleys, and rows of buildings, sometimes aid the collector by channeling emissions. When these features are associated with a particular facility, their downwind side is a suitable place to collect a sample because the emission remains more concentrated further from the release point.
f. For collection in a possibly contaminated location, and if the situation permits, initially use a detection kit such as the M18A2/M256AI to determine if a possible vapor hazard exists from known chemical agents. Also, use the kit when personnel are required to examine possible toxic agent munitions. In any case, collect air samples with the white-band tubes and save for identification and analysis.
g. Small air samplers also enable the collector to obtain vapor samples from alleged toxic agent munitions at a safe distance while explosive ordnance disposal (EOD) operations are performed. If EOD personnel are not on the scene, the air sampler can be activated, and the collector can stand at a safe distance while the sampler is operating.
h. Perform sampling operations as soon as possible when directed by a higher headquarters or after suspected chemical or biological contamination is encountered.
a. Water sampling is a matter of collecting enough water to get acceptable information about the contaminants. The collector should provide the analysis center with one C18 and one silica cartridge when using the Sep-PakTM technique or 100 ml in a sterile bottle when Sep-PakTM is not available.
b. General guidelines: If it is believed that the threat has used standard chemical agents during an attack, use the M272 chemical agent water test kit for initial screening and sampling.
c. When collecting water samples using the Sep-PakTM C18 cartridge, the following items are required:
d. Prior to collecting each sample, prime the Sep-PakTM system in the following manner:
e. After priming the Sep-PakTM, assemble the components in the following configuration:
f. Use the following procedures to collect samples with Sep-PakTM:
NOTE
You should take a minimum of four samples: three samples of the suspected contamination and one control sample from a nearby unaffected (none contaminated) area for reference.
g. For samples to be representative of the overall contaminated area, the collection point should be carefully selected. Collect samples from—
NOTE
If an oil film, globules of organic materials, or an unnatural appearing powder-like material is visible on the water's surface, collect a surface sample of the material. If not, collect the sample from near the bottom of the water source (stream, lake, pond, water container). The upper layers of water may have lesser amounts of contaminants, due to higher temperatures that promote decomposition. Since most chemicals of interest are more dense than water, contaminants usually sink to the bottom of the water source.
h. Collect the sample without the Sep-PakTM by immersing a capped or stoppered container to the desired depth, removing the cap or stopper, letting the container fill, and then capping the container. An alternate method for deeper water is to use a plastic, pump-operated siphon to pump water from a specific depth.
i. The best time to collect a sample of water from a location is when intelligence or local reports indicate that a process of possible interest is ongoing. In the absence of reliable reporting, this may be indicated by increased activity, higher than normal amounts of security, or increased flow from facility chimneys or water discharge pipes. In field areas where a toxic agent has been sprayed or disseminated over a land area, the best time to collect water samples is just after the start of a rainstorm when runoff is beginning. Natural surface drainage will concentrate any remnants of toxic compounds in depressions, streams, or ditches.
Soil is a suitable medium to collect as samples for toxic organic compounds. A critical point, however, is that the precise site of the agent deposition must be sampled for best results. Contamination may be recognized by discoloration or apparent deposition of material on the soil's surface. If discoloration or deposits of material are evident, only collect the discolored soil or deposited materials, if possible. Dead, malformed, and wilted foliage is an indicator of contamination. Soil samples should be collected from open areas, along the drip line tents, stationary equipment, bottom of ditches and terrain depressions.
a. Collect the soil samples by using a knife, spoon, spatula, or similar item to scrape a square of topsoil (2×5×1 centimeters) from areas that appear to have been contaminated in to a collection container. If chunks or clods of earth are collected, select those that are no larger than 10×5×1 centimeters (see Table B-4). Also, collect a control sample of soil of the same type and texture from a nearby uncontaminated area.
b. Use a glass bottle, jar, or TeflonTM jar as the container when available. When these containers are not available, Mylar bags may be used. When using a glass bottle, jar, or TeflonTM jar, seal the cap with either pressure-sensitive or TeflonTM tape, and mark for identification. When using Mylar bags, place each sample in a separate bag, push excess air out, and seal by folding the open end over two to three times and wrapping the bag with tape. Insert the first bag into a second bag, seal, tape, and mark for identification. If possible, place the samples in a piglette.
CAUTION
Avoid direct contact with the sample to prevent exposing yourself to the suspect agent (MOPP 4 is required).
c. Collect samples as soon as possible when directed, upon detection of a suspect substance, or after the alleged incident.
As with soil samples, vegetation is also a suitable medium to collect as samples for toxic organic compounds.
a. Collect samples of vegetation that appear to be different from normal. Select leaves that have wilted or appear to have been chemically burned. Collect samples of vegetation that appear to have liquid or solid substances deposited on their surfaces (this may be noticed as a shiny or moist area).
b. Collect samples of vegetation at several locations within the suspected contaminated area. Using a cutting tool or any sharp object, cut several affected leaves and/or a handful of grass whenever possible. Do not crush the sample. Place the sample into a Mylar or reclosable bag. Squeeze excess air out of the bag and seal it. Fold the open end of the Mylar bag over two to three times, and wrap it with tape. The minimum size for a sample is three leaves or three handsful of grass. One leaf is of little value, but is better than nothing. Bark is acceptable but not preferred. Mark the bag for identification. Take a control sample of similar material from an unaffected (uncontaminated) area. Fold, seal, tape, and mark the control sample in the same manner as the actual sample.
c. When it is possible to determine a probable center of attack in an area, collect vegetation samples near the center of the area, about 100 meters upwind of the area, and in several 100-meter increments downwind of the area. If the collector can discern a contamination pattern in the area, this should be reported.
a. Just as blood and urine specimens are taken from humans who were allegedly exposed in an attack, also collect specimens from individuals who claim not to be affected by a toxic agent and are from the same group as exposed personnel. The purpose is the same as collecting environmental control specimens; that is, to determine if a toxic substance is present in the individuals' natural environment or if it has been artificially introduced.
b. Selection of humans for control sampling is somewhat more complicated than selection of environmental control samples. This is because ethnic diets, racial differences, physiological makeup, and actual living conditions of persons who are outwardly similar may introduce potentially large deviations. Each of these factors must be accurately considered before selecting subjects as controls.
c. Consideration of ethnic diets is important because of unique foods or methods of food preparation that may exist. As an example, individuals in settled areas may purchase beer that has been carefully filtered and sterilized, while individuals in a nearby unsettled area may ferment their own beer by burying home crafted jugs in the ground and extracting the product little by little over several months.
d. Racial differences can account for differences in mortality and morbidity rates in specific populations. One example of this could be the high rate of hemophilia in a population versus the rarity of the disease in another.
e. Physiological makeup is critical because of the differences in hormone balance and tissue composition in males, females, adults, and juveniles. For this reason, medical control specimens should be drawn from individuals of the same gender and approximate age as specimens from exposed personnel, if possible.
f. Differences in the actual living conditions of people also require a close look. The point here is that conditions in remote, semicivilized camps are seldom the same as those in a well-established camp that has access to modern amenities.
g. The bottom line in selecting subjects for medical control sampling is that they be as similar in all aspects as possible.
a. Trained medical technicians or physicians should collect medical specimens (human or animal); however, Special Forces NBC Reconnaissance team personnel are trained to do this procedure. Remember, the collector must have express permission (authority) to collect medical specimens from the dead, because of religious beliefs in many cultures. To obtain such specimens without permission may result in unnecessary mission complications. Ensure all personnel handling or collecting medical specimens have received proper immunizations for their own protection. They must be inoculated IAW The Surgeon General's guidance.
b. Medical specimens collected during an investigation include blood, urine, sputum, nasal swabs, and tissue specimens from living victims and blood and urine specimens from unexposed persons (background control specimens).
c. Collect blood specimens using either a standard 10 cc disposable syringe with a 1- to 1½-inch needle (20 to 22 gauge), or by using a VacutainerTM system. When using a VacutainerTM system, ensure that multiple specimen needles and "red top" vacuum tubes are used. Ten cc of blood is sufficient for analytical testing. Do not take more than 5 cc from small, malnourished children. After blood is collected, it should be transferred to a polypropylene-type container and sealed with parafilm before transporting. All body fluids should be collected without violating antiseptic techniques. Also, prior to transporting specimens, collectors need to check specimen containers for paper labels IAW guidelines for labeling medical specimens. Collect blood specimens using the following materials equipment: