SWRHL-34r

CALCIUM IN HOCK JOINTS OF WILDLIFE RUMINANTS
   IN SELECTED AREAS OF THE UNITED STATES
                          by
                Raymond A. Brechbill,
                 Ronald E. Engel and
                  Robert  C. Kramp
         Bioenvironmental Research Program
      Southwestern Radiological Health Laboratory
              U.  S. Public Health Service
     Department of Health, Education,  and Welfare
                  Las Vegas, Nevada
                     July 21, 1967
      This study performed under a Memorandum of
             Understanding (No. SF 54 373)
                        for the
         U. S.  ATOMIC ENERGY COMMISSION

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                          LEGAL NOTICE


 This report was prepared as an account of Government sponsored
 work.  Neither the United States, nor the Atomic Energy Commission,
 nor any person acting on behalf of the Commission:

 A.   Makes any warranty or  representation, expressed or implied,
 with respect to the accuracy, completeness, or usefulness of the in-
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 fringe privately owned rights; or

 B.   Assumes any liabilities  with respect to the use of, or for damages
 resulting from the use of any information, apparatus, method,  or pro-
 cess disclosed in this report.

 As used in the above, "person acting on behalf of the Commission" in-
 cludes  any employee or contractor  of the  Commission,  or employee
 of such contractor, to the extent that such employee or contractor  of
 the  Commission,  or employee of such contractor prepares,  dissemin-
 ates, or provides access to, any information pursuant to his employ-
 ment or contract with the Commission,  or his employment with such
 contractor.
0'78

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                                                 SWRHL-34r
CALCIUM IN HOCK JOINTS OF WILDLIFE RUMINANTS
   IN SELECTED AREAS OF THE UNITED STATES
                         by
                Raymond A.  Brechbill,
                 Ronald E.  Engel and
                  Robert C. Kramp
         Bioenvironmental Research  Program
     Southwestern Radiological Health Laboratory
             U. S. Public Health Service
     Department of Health, Education, and Welfare
                  Las Vegas,  Nevada
                    July 21,  1967
      This study performed under a Memorandum of
             Understanding (No. SF 54 373)
                        for the
        U. S. ATOMIC ENERGY COMMISSION

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                      ACKNOWLEDGEMENTS






The authors are grateful to the following conservation agencies and



individuals for their generous  cooperation in furnishing the wildlife



ruminant hock joints which were utilized for this study:  U. S.  Fish



and Wildlife Service, Fort  Niobrara Wildlife Refuge; Kofa  Game



Range;  National Bison Range;  National Elk  Range; Wichita Wild-



life Refuge; San Andres  National Wildlife Refuge; Desert Game



Range;  U.S. Forest Service, San Bernardino National Forest;



Nebraska State Game  Forestation and Parks Commission;  Idaho



Fish and Game Department;  Nevada Fish and Game Commission;



Oregon State Game Commission; Minnesota Department of Conser-



vation - Section of Game; Utah Fish and Game; Kentucky - Depart-



ment  of Fish and Wildlife Resources;  and Mr. Patrick J.  Ray,



Westwood, Massachusetts.





This work was done as part of a U.  S.  Public Health Service radi-



ation  surveillance study  of wildlife ruminants in the Nevada Test



Site environs under a  Memorandum of Understanding,  SF 54 373,



between the Atomic Energy Commission and the U. S. Public



Health Service,  Las Vegas,  Nevada.

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                            ABSTRACT






The percent calcium of bone ash found in hock joints of 63 mule



deer (Odocoileus hemionus),  14 white-tailed deer (Odocoileus



virgianus),  14 elk (Cervus canadensis), 13 desert bighorn sheep



(Ovis canadensis nelsoni), 9 antelope  (Antilocarpa americana),



and 7 buffalo (Bison bison) is reported.  The average calcium con-



tent of hock joints in the 6 species from 18 different areas through-



out the United States was 37. 6% of bone ash.  Differences between



species,  regardless of geographic locations, were small when



present.
                                11

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                      TABLE OF CONTENTS







ACKNOWLEDGEMENTS                                          i



ABSTRACT                                                     ii



TABLE OF CONTENTS                                         iii



LIST OF TABLES                                               iv



INTRODUCTION                                                 1



MATERIALS AND METHODS                                     2



RESULTS AND DISCUSSION                                      4



SUMMARY                                                       7



REFERENCES                                                   8
                                111

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                        LIST OF TABLES
Table 1.  Percent calcium of ashed bone reported in literature.    1

Table 2.  Percent calcium in bone ash by species and  geograph-
          ical location.                                           4

Table 3.  Percent calcium/bone ash in various species regard-
          less of location.                                        5

Table 4.  Percent calcium in bone ash found in hock joints of
          mule deer by sex.                                      6

Table 5.  Percent calcium in bone ash found in hock joints of
          mule deer by age class.                                6
                                IV

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                         INTRODUCTION

The assessment of 9°Sr levels in bones of mammals has been expressed
in various units,  e.g., pCi 90Sr/gm calcium, pCi  9°Sr/gmbone ash,
pCi 90Sr/gm wet bone (fresh bone), pCi 9°Sr/gm dried bone.   A great
many of the earlier reports list  9°Sr levels in bone as  pCi of  90Sr/gm
of calcium (strontium units).  However, when reported  in pCi  9°Sr/gm
bone ash, calcium content is not normally determined.  In comparing
data presented in  strontium units with that in pCi of  9°Sr/gm bone ash
where the percent calcium is not  given, one must use an assumed
constant percent (Ca/gm bone ash) to convert either unit to the other.
Values  reported in the literature  for wildlife ruminants indicate that
bone ash contains  from 37.4% to 38. 8%  calcium depending on what bone
of the skeleton is analyzed and from what species the bone is  collected.
(Table 1).

Table 1.  Percent calcium of ash bone  reported in literature.	
_   .               Number of        Bone      % Ca in
Species             ci        c            -DAT.  Reference
	Samples	Specimen	Bone Ash	
Deer               Not given      Hock  Joint  38. 7         Lindberg
Animals*          Not given      Not given   38.8_+.50** Holtzman  '
White-tailed deer      18          Mandible    37-4  +. 16*** Shultz
White-tailed deer      18          Antler      36. 2  +. 28*** Shultz

*Species not given.   **Explanation of plus or minus value not reported
.  , , _        ,   ,         ,  ,                     in original reference.
i-vvOne standard error of the mean.

The primary objective of this study was to determine the calcium con-
tent in hock joints of various wildlife species and to determine if these
values were species or geographically dependent or both.  This infor-
mation is necessary to aid in determining whether our  9^5r values are
a reflection of true fallout,  species differences, analytical error,  or
calcium deficiency and to enable comparison of our findings with those
reported in the literature as strontium units.
                                 1
Note:  pCi = pico curie.

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                   MATERIALS AND METHODS

During the fall and winter hunting  season of 1965,  120 wildlife ruminant
hock joints were received from various conservation agencies throughout
the United States as well as from interested individuals.  The  samples
were obtained from the Northeastern United States,  Oklahoma, Montana,
Nebraska, Kentucky,  Nevada,  Utah,  Minnesota, Oregon,  Idaho, Kansas,
Arizona,  and California.
The samples were taken  from the  right or left leg of the animal by
cutting the bone at a point four inches above and below the hock joint.
All skin and  attached muscular tissues were removed prior to analysis.
Calcium analysis was performed by the United States Public Health
Service, Southwestern Radiological Health Laboratory, Las Vegas,
                                           (4)
Nevada.   The technique  developed by Johns    is included in detail
because it is a modification of the  classic calcium oxalate technique   .
The bone  sample is ashed at  500°C in an  electric furnace.  A 1. 00 gram
portion of the ground bone ash is then dissolved in 6N HC1.  Fifty ml
of saturated  oxalic acid  solution is added and the pH adjusted to 3. 0
with 6N ammonium hydroxide to precipitate calcium oxalate.  The
solution is allowed to  stand for 12-24 hours to permit the  precipitate
to settle.  The supernatant is removed by filtration and the calcium
oxalate precipitate washed several times  with 0. 5% ammonium oxalate.
The precipitate and filter paper are placed  in a muffle furnace and
heated to  500°C for conversion of  calcium oxalate to the calcium oxide.
The ash is then dissolved in dilute nitric  acid and diluted  to 250ml with
deionized water.  A 5ml  subsample is diluted to approximately 50ml,  to
which  5ml 6N potassium  hydroxide is added, and the solution allowed

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to stand for at least 3 minutes.  One-tenth gm (Cal-Red Indicator



Dilute*) is then added, and the solution titrated with 0. 1M



ethylenediaminetetraacetate disodium salt (EDTA Salt).  The EDTA



Salt solution is  standardized against a CaCO3 primary standard using



the same  buffering and titration procedure.




Percent calcium in bone ash is calculated according to the following



formula:



                        ml EDTA Salt x M EDTA Salt x  40. 1 x 100
% calcium in bone ash =
                              Sample weight in grams x 1000
*Registered Trade Mark, U. S. Patent Office, Washington, D.  C.




                                 3

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                        RESULTS AND DISCUSSION


    The average calcium content of six species from 18 different geo-

    graphic areas are arranged in descending order (Table 2).   The high-

    est and lowest mean value, a difference of 2. 2%, consisted of only

    one  sample each.  If these two are disregarded, the difference be-

    tween the buffalo (Montana) and the mule deer(Southeast Oregon) is

    0.9%. A statistical test of the difference between mean values

    failed to show a significant difference among species from various

    locations.

    Table 2.  Percent calcium in bone ash by species and geographical
              location.
Species
Buffalo*
Buffalo
Elk
White-tailed deer
White-tailed deer
Elk
Antelope
Elk*
White-tailed deer
Mule deer
Mule deer
Mule deer
Mule deer
Elk*
Antelope
Desert bighorn sheep
Mule deer
Mule deer
Mule deer
Mule deer
Mule deer
Mule deer
Desert bighorn sheep*
Mule deer*
Location
Oklahoma
Montana
Montana
Nebraska
Kentucky
Oklahoma
Montana
Southern Nevada
New England states
Utah
Nebraska
Southern Nevada
Minnesota
Northeastern Nevada
Northern California
Arizona
Idaho
New Mexico
Southern California
Northern Nevada
Northwest Oregon
Southeast Oregon
Southern Nevada
Northeast California
X% Ca in No. of
Bone Ash Samples
38.8
38. 1
38. 1
38. 0
38. 0
38.0
38. 0
37.8
37. 7
37. 7
37.6
37. 5
37. 5
37. 5
37. 5
37.4
37.4
37.4
37.4
37.4
37.4
37.2
37.2
36.6

37. 5-38. 8
37. 7-38.4
37. 3-39. 0
37. 7-38. 2
36. 9-39. 3
37. 7-38.4
37. 3-38.2
37. 3-38.4
36. 9-38. 1
36. 7-38. 1
36.4-38.4
36.9-37.9
37. 3-37. 7
37. 1-38.4
36. 6-37.9
36.9-37. 7
36.9-38. 2
36.9-38.4
36. 7-38.0
35.8-37.9
36. 7-37. 7
36. 2-38.0

1
6
4
6
4
6
5
2
4
6
3
12
6
2
4
5
6
6
4
8
6
5
2
1
*Inadequate number of samples to be included in statistical analysis,

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The percent calcium in bone ash in various species regardless of location

are listed in Table 3. The buffalo, white-tailed deer and elk have the

highest values while  the antelope,  mule deer and desert bighorn sheep

have the lowest.  It is interesting that, in general, the buffalo, white -

tailed deer and elk are animals from higher rainfall  regions.  Generally

it is assumed that areas of calcium deficiency occur in areas of high

rainfall where the calcium carbonates have been leached from the soil.

Our data show that the calcium content in the hock joints of animals

browsing in these areas do not have  lower  values than those animals

grazing in areas  of low rainfall.


Table 3.  Percent calcium/bone ash in various  species regardless of
          location.
Species
Desert bighorn sheep
Mule deer
Antelope
Elk
White-tailed deer
Buffalo
X% Ca in Bone Ash
37. 3
37.4
37,8
37.8
37. 9
38.2
s*
0. 536
0. 529
0.488
0.441
0.476
0.453
No. of
Samples
13
63
9
14
14
7
'"standard deviation

The average calcium content in the mule deer hock joints is identical

for both male and females (Table 4).  Perhaps this is a reflection of

the calcium drain on the body of the male mule deer during antler

formation, which under certain conditions may be equal to the calcium

drain of the lactating female mule deer.   Females show a greater

variance (Table 4) than do the males probably because both lactating

and non-lactating does were sampled.

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Table 4.  Percent calcium in bone ash found in hock joints of
          mule deer by sex.
Sex
Male
Female

X % Ca in Bone Ash
37.
37.

4
4

36
35

Range
. 7-38.4
. 8-38. 1


0.
0.

s*
504
579

No. of
Samples
27
31
Total 58**
* standard deviation
**total hock joints that were identified by sex.

The calcium content in bone ash of mule deer hock joints is arranged
by age class in Table 5.  Examination of the mean values indicates
an apparent increase in calcium content from the  0. 5 year age class
(fawns) to the 3. 5 year age class (maturity), then a decrease in
animals above that age class.  However, it was not possible to verify
the increase statistically due to  the large variation of % Ca values

within each age  group (as indicated by the ranges  shown).  The factors
contributing to this  variation,  in order of importance, are the group-

ing of animals into half-year age groups,  the natural animal to animal
variation and  the error of the method of chemical analysis.

Table 5.  Percent calcium in bone ash found in hock joints of mule
          deer by age class.
Age X%Ca
0. 5 years
1.5 years
2.5 years
3. 5 years
4. 5 years*

in Bone Ash
37. 0
37. 2
37.6
37. 7
37.4

Range
35.8-37. 9
36.4-38. 1
36. 7-38.2
36.9-38.4
36.6-38. 1

No. of Samples
7
12
7
7
22
Total 55**
* 4. 5 years or greater.
**total hock joints that were identified by age.
It is apparent that by increasing the number of samples of certain species
from several  locations, little would be gained as no significant differences
were noted in calcium content among  species,  location or sexes where there
was an adequate sample size for statistical analysis.   The data obtained
during this study will serve as background as well as an aid in com-
paring our data with that of others.

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                            SUMMARY






The average calcium content of hock joints in six species of wild-



life ruminants from 18 different areas was 37. 6% of bone ash.



Differences between species, regardless of geographic locations,



were  small when present.

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                          REFERENCES
(  Lindberg, R.G.  and J.G. Olafson,  1958.  Preliminary Report  --The

  Occurrence of 9°Sr in Nevada Deer Herds.  University of California at

  Los Angeles, U.S.  AEC Report, unpublished.



  Holtzman, R. B. , 1963.  Desirability of Expressing Concentrations of

  Mineral-seeking Constituents of Bone as a Function of Ash Weight.

  Health Physics,  8(3): 315-319.



  Schultz, V. ,  1965.   Comparison of Strontium -- 90  Levels Between

  Antler and Mandible of White Tail Deer.  J. Wild.  MGMT 29(1) 33-38.


(4\
  Johns,  F. B. ,  et al,  1962.  A Rapid Determination of Calcium Using

  Ethylenediaminetetraacetate (Di-sodium salt) as a Titrant.  U.S. Public

  Health Service, Southwestern Radiological Health Laboratory, Las

  Vegas, Nevada,  unpublished.



  'Scott, W.W.,  1955.  Standard Methods of Chemical  Analysis.  Volume I,

  D. Van Nostrand Company,  Inc.  pp.  211-12.

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    20  R. C. Emens, NTS Support Office, AEC, Mercury, Nevada




    21  Martin B. Biles, DOS,  USAEC, Washington,  D.  C.




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    24  G. D. Ferber, ARL,  ESSA, Washington, D. C.




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    26  James G. Terrill, Jr. , Director, NCRH, PHS, Rockville,  Maryland




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    28  Bernd Kahn,  NCRH,  RATSEC,  Cincinnati, Ohio




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    32  Northeastern Radiological Health Lab. ,  Winchester, Mass.




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     37  Mail & Records, NVOO/AEC, Las Vegas, Nevada

     38  Paul T. Tueller,  University of Nevada,  Reno, Nevada

     39  Charles Hanson, U S Fish and Wildlife Service, Las  Vegas, Nev.

     40  V. R. Bohman, University of Nevada, Reno,  Nevada

     41  Bruce Browning,  California Fish  & Game Dept. ,  Food Habit
              Laboratory,  Sacramento, California

     42  George Welsh,  Arizona Fish and Game Dept. , Kingman, Arizona

     43  Al Jonez,  U S Bureau of Reclamation, Boulder City,  Nevada

     44  Fred Isbell, U S Forest Service,  Las Vegas, Nevada

     45  District Supervisor, Nevada Fish & Game Commission, Las Vegas, Nev.

     46  Director,  Nevada Fish &  Game Commission, Reno, Nevada

     47  Director,  National Park Service,  Boulder City; Nevada

     48  District Manager,  U S  Bureau of Land Management,  Las Vegas,  Nev.

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     50  University of Nevada Library, Reno and Las  Vegas,  Nevada

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     53  R.  S. Davidson, Battelle  Memorial Institute, Columbus, Ohio

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