Lecture 37
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Isotope Hydrology
Hydrogeochemical Cycle
Common Isotopes Used in Hydrologic Studies
Global Distribution
Tritium
Nitrogen
Environmental Isotope Uses
Case Studies
A depiction of the hydrogeochemical cycle.

Distribution of mean d 18O of precipitation, based on stations having at least

Hydrogen and oxygen isotopic content of ocean water and precipitation. Due to
kinetic isotope fractionation during evaporation of moist oceanic vapor, the hydrogen
and oxygen isotopic content of water vapor above the oceans is -86 and -12,
respectively. The isotopic content of precipitation is in isotopic equilibrium with
vapor in a cloud. Thus, the d D and d 18O values of the first rain are -14 and
-3, respectively, depleting the cloud in D and 18O as precipitation occurs. Therefore,
precipitation becomes isotopically lighter and lighter as it is continuously removed
from clouds.
Monthly weighted mean d 18O of a coastal (Hatteras) and an inland (Flagstaff)
station. The moderating effect of the ocean upon temperature is evident in the
low variability of the Hatteras d 18O data.
Approximate range (in years) of dating applications of selected environmental
Deposition in TU-meters of tritium across the continental United States
from 1953 to 1983. U.S. Geological Survey sampling stations listed are
Albuquerque, NM (ALB), Boston, MA (BOS), Cape Hatteras, NC (CAHAT),
Chicago, IL (CHI), Lincoln, NE (LINC), Madison, WI (MAD), Menlo Park,
CA (MENPK), Ocala, FL (OCALA), Portland, OR (PORT), Salt Lake City,
UT (SLC), Saint Louis, MO (STL), Waco, TX (WACO), and
Monthly tritium concentration in precipitation at Ottawa, Canada, 1953 through 1985.
Range of nitrogen isotope composition for different sources of dissolved nitrogen
Average Terrestrial Abundance of Isotopes Used in Hydrogeologic Studies
| Element |
Isotope |
Average Terrestrial Abundance (atom %) |
Comments |
| Hydrogen | 1H |
99.985 | |
2H |
0.015 | ||
3H |
<10-14 | Radioactive, t1/2 = 12.43 years | |
| Helium | 3He |
0.00014 | |
4He |
99.99986 | ||
| Carbon | 12C |
98.90 | |
13C |
1.10 | ||
14C |
<10-10 | Radioactive, t1/2 = 5,715 years | |
| Nitrogen | 14N |
99.63 | |
15N |
0.37 | ||
| Oxygen | 16O |
99.762 | |
17O |
0.038 | ||
18O |
0.200 | ||
| Silicon | 28Si |
92.23 | |
29Si |
4.67a | ||
30Si |
3.10 | ||
32Si |
<10-12 | Radioactive, t1/2 = 172 years | |
| Sulfur | 32S |
95.02 | |
33S |
0.75a | ||
34S |
4.21 | ||
35S |
<10-11 | Radioactive, t1/2 = 82 days | |
36S |
0.014a | ||
| Chloride | 35Cl |
75.77 | |
36Cl |
<10-12 | Radioactive, t1/2 = 300,000 years | |
37Cl |
24.23 | ||
| Strontium | 84Sr |
0.56a | |
86Sr |
9.86 | ||
87Sr |
7.00 | ||
88Sr |
82.58a | ||
| Uranium | 234U |
0.0055 | Radioactive, t1/2 = 247,000 years |
235U |
0.72 | Radioactive, t1/2 = 71.3 x 106 years | |
238U |
99.27 | Radioactive, t1/2 = 4.51 x 109 years |
Source: IUPAC (1992).
aThese isotopes are presently not used in ground-water studies.
Ground-Water Problems Aided by Environmental Isotopes
Stable Isotope |
Radioactive Isotopes |
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| Type of Problem | d D | d 13C | d 15N | d 18O | d 34S | d 87Sr | 3H | 14C | 36Cl | 39Ar | 85Kr | U-diseq | |||
| Recharge and Flow Rate | |||||||||||||||
| Unsaturated zone | C | C,a | B,b | ||||||||||||
| Arid Zones | C,c | B,b | |||||||||||||
| Exchange of river and lake water | |||||||||||||||
| with ground water | C,d | C,d | C,e | C,e | |||||||||||
| Average ground-water rate in | |||||||||||||||
Systems less than 5 years old |
A,f | A,f | C,f | ||||||||||||
Systems between 5 and 30 years old |
A,g | C | B,b | ||||||||||||
| Characterization of a Gound-Water Mass | |||||||||||||||
| Local area less than 30 years old | C,h | C,h | C,i | C,i | B,b | ||||||||||
| Regional systems | A,j | C,k | A,j | C,l | B,b | ||||||||||
| Identification of Recharge Area or Source of Water | |||||||||||||||
| Local area | A,m | C,n | A,m | C | C,o | C,o | B,b | ||||||||
| Regional systems | A,p | C | A,p | C | B,b | ||||||||||
| Leakage between Aquifers | C,q | C,q | |||||||||||||
| Investigations of Ground-Water Flow in Fractured Rocks | |||||||||||||||
| Carbonate karst rocks | A,r | A,r | A,r | ||||||||||||
| Noncarbonates | A,s | A,s | A,s | C | |||||||||||
| Evaluation of Ground-Water Flow and Storage Characteristics | |||||||||||||||
Local system: well-mixed reservoir or piston flow |
A,t | ||||||||||||||
| Dispersivity investigations | C | C | C | C | |||||||||||
| Separation of Stream Discharge into Ground-Water and Surface-Water Components | A,u |
A,u |
A,u |
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| Sources of Dissolved Constituents | A,v | A,w | A,v | A,aa | B,x | C,v | B,b | ||||||||
| Geochemical Reaction Modeling | A,y | C,y | |||||||||||||
| Ground-Water Dating | |||||||||||||||
| Less than 5 years | A,p | C,n | A,f | A,u | B,bb | ||||||||||
| 5-50 years | A,g | C,i | B,b | B,bb | |||||||||||
| 50-1,000 years | C,bb | ||||||||||||||
| 1,000-40,000 years | A,z | A,z | A,cc | ||||||||||||
| 60,000-1,200,000 years | B,dd | C,ee | |||||||||||||
| Key for Remarks | |
| Frequency of Use in Ground-Water Studies | |
A Has been useful in many studies |
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B Has received some use; looks promising for future studies as technology improves |
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C Has received some use |
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| Example Applications | |
a Munnich (1983) b Bentley, Phillips, and Davis (1986) c IAEA (1980) and Gvirtzman and Magaritz (1986) d Payne (1983), Stichler and Moser (1979), Carlin et al. (1975), Krabbenhoft et al. (1990), and Darling, Allen , and Armannsson (1990) e Carlin et al. (1975) f Stichler and Moser (1979) and Schotterer et al. (1979) g Rauert and Stichler (1974), Fontes (1980), Phillips et al. (1989), and Solomon and Sudicky (1991) h Payne, Quijano, and Latorre (1979) i Fontes (1980) and Pearson et al. (1991) j Airey et al. (1979), Gat (1971), and Pearson et al. (1991) k Lloyd and Howard (1979) l Fontes (1980) m Schotterer et al. (1979), and Muir and Coplen (1981) n Letolle and Olive (1983) o Fontes (1980)
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p Payne (1983, Gat (1971), Pearson et al. (1991), and Darling, Allen, and Armannsson (1990) q Payne (1981) r Davis et al. (1970) and Fontes (1983) s Schotterer et al. (1979) t Martinec et al. (1974) u Sklash and Farvolden (1979 and 1982), Kennedy et al. (1986), and Stewart and McDonnell (1991) v Payne (1983), Payne, Quijano, and Latorre (1979), and Simpson and Herczeg (1991) w Heaton (1986) and Hübner (1986) x Pearson et al. (1991) and Starinsky et al. (1983) y Plummer et al. (1990) and Plummer, Prestemon, and Parkhurst (1991) z Buchardt and Fritz (1980) and Pearson et al. (1991) aa Claypool et al. (1980) bb Pearson et al. (1991) and Chapter 11 cc Fontes (1983), IAEA (1983a), and Pearons et al. (1991) dd Pearson et al. (1991), Torgersen et al. (1991), and Nolte et al. (1991) ee Pearson et al. (1991) |