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RESEARCH· ·1970·

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B178<br />

terranes where the search for nickel is most likely to<br />

be concentrated.<br />

REAGENTS<br />

The assumption is made that readers interested in<br />

this method are familiar with the philosophy underlying<br />

the design and use of geochemical methods as<br />

well as the basic equipment and techniques necessary<br />

for the operation of a geochemical laboratory. Those<br />

individuals who need additional information may refer<br />

to Ward, Lakin, Canney, and others (1963).<br />

The quantities suggested below are sufficient for 100<br />

analyses. Reagent-grade chemicals and demineralized<br />

water should be used.<br />

Buffer solution: Dissolve 50 g of ammonium citrate [ (NH,)ll<br />

HC6HG07] in 550 ml of water. Add 85 ml of cone NH40H, and<br />

mix. (Ammonium hydroxide is added before sodium thiosul·<br />

·fate to prevent the precipitation of sulfur.) Dissolve 200 g of<br />

sodium thiosulfate (Na2S203·5H20) in the solution, and then<br />

add additional cone NH10H to give a pH of 10.0. Add 4N<br />

NaOH until the pH is 10.8-11.0. Finally, dilute the solution<br />

to !liter with water.<br />

a-Furildioxime solution, 0.2 percent: Dissolve 0.4 g of<br />

a-furildioxime in 30 ml of 95-percent ethanol, and dilute this<br />

solution to 200 ml with benzene.<br />

Hydrogen peroxide, 30 percent. (See section, "Interfering<br />

elements.")<br />

Nitric acid, 4N: Dilute 25 ml of cone HN03 to 100 ml with<br />

water.<br />

Sodium hydroxide solution, 4N: Dissolve 40 g of sodium hydroxide<br />

pellets in enough water to make 250 ml of solution.<br />

Standard nickel solution (100 pg per ml) : Dissolve 0.2 g of clear<br />

unetHoresced crystals of nickel cllloride (NiCl2·6H20) in 500<br />

ml of O.lN HCI. From this solution prepare more dilute standard<br />

solutions (10 ,ug/ml and 1 ,ug/ml) prior to preparing the<br />

series of nickel standards.<br />

PROCEDURE<br />

The following procedure is given in terms of a single<br />

sample. When batch operation is used, the length of time<br />

of contact ·between sample and either acid or buffer is<br />

critical and must be closely controlled; therefore, steps<br />

. 2-5 should be performed on no more than five samples<br />

at a time. Once the nickel complex has been extracted,<br />

large batches of sample solutions can be accumulated<br />

before the estimation step is carried out.<br />

1. Place a 0.2-g (weighed) or 0.2-cc (scooped) quantity<br />

of sample in a 25 X 100-mm test tube.<br />

2. Add 1 ml ·of 4N HN0 3 to the tube.<br />

3. Slosh the sample and acid for 30 seconds.<br />

4. Add 10 ml of buffer solution and mix.<br />

5. Add 2 ml of a-furildioxime solution, stopper the<br />

tube, and shake it vigorously for 30 seconds.<br />

6. Compare . the color in the floating benzene layer<br />

visually against the standard series. Centrifuging<br />

the tube aids in breaking up any emulsion that<br />

ANALYTICAL METHODS<br />

may form and is strongly recommended for<br />

samples that contain much organic matter.<br />

7. Calculate the content of readily extractable nickel<br />

according to the following formula :<br />

Parts per million (ppm) =<br />

micrograms (p.g) of nickel found<br />

sample weight (g) or sample volume (cc)<br />

Results are expressed as ppm weight/weight<br />

if a weighed sample is used, and as ppm weight/<br />

volume if a scooped sample is used. The density of<br />

sieved soil or sediment samples is often about 1,<br />

except for organic-rich samples, so ppm (w/w)~<br />

ppm (w/v).<br />

PREPARATION OF STANDARDS<br />

1. To a series of 25 X 100-mm test tubes add 1 inl of 4N<br />

nitric acid.<br />

2. From the appropriate nickel standard solutions<br />

transfer, respectively, 0, 0.1, 0.2, 0.4, 0.8, 1.5, 3.0,<br />

6.0, and 12.0 p.g of nickel to the above series.<br />

3. Add 10 ml of buffer to each tube and mix.<br />

4. To each tube add 2 ml of a-furildioxime solution,<br />

stopPer the tube, and shake it vigorously for 30<br />

seconds.<br />

These standards are normally stable for several days<br />

and must be kept tightly capped to prevent solvent<br />

evaporation. Screwcap test tubes are suggested.<br />

DISCUSSION<br />

Data produced by cold methods of this type are useful<br />

in a relative sense only; there are no "correct"<br />

results as this term is conventionally used. Therefore,<br />

every sample must be treated as nearly alike as possible<br />

to a void varying degrees of bias in a data set. V ariability<br />

in the time of extraction is a well-known major<br />

source of bias in cold-extractable field tests; consequently<br />

the extraction time should be closely controlled.<br />

Stability of :reagents<br />

The buffer solution loses ammonia very readily, with<br />

consequent drop in pH, and thus the buffer must be<br />

kept in a closed container when not in use and the pH<br />

must be checked as frequently as conditions of temperature<br />

and use demand.<br />

The a-furildioxime solution is reasonably stable and<br />

does not deteriorate appreciably over a period of a few<br />

days even when kept at room temperature and exposed<br />

to light. When first prepared, the reagent solution<br />

usually is slightly yellow. A solution that is allowed to<br />

stand for a period of several weeks will first become<br />

darker yellow and then will gradually turn to orange.

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