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Enzyme  Activity  as  an  Index  of  Growth 
Superiority  of  Firms  clausa  var.  clausa  on  Two  Soils 


« 

By 

RUSSELL  MacBAIN  BURNS 


A DISSERTATION  PRESENTED  TO  THE  GRADUATE  COUNCIL  OF 
THE  UNIVERSITY  OF  FLORIDA 
IN  PARTIAL  FULFILLMENT  OF  THE  REQUIREMENTS  FOR  THE 
DEGREE  OF  DOCTOR  OF  PHILOSOPHY 


UNIVERSITY  OF  FLORIDA 
1971 


ACKNOWLEDGEMENTS 


I thank  the  members  of  my  supervisory  committee,  particularly 
Drs.  Spinks,  Hortenstine,  and  Hammond,  for  their  encouragement  and 
patience.  My  special  thanks  go  to  Dr.  William  Pritchett,  Chairman 
of  the  Committee,  for  providing  guidance  during  early  stages  of 
research  and  for  his  assistance  in  preparing  this  manuscript;  to 
Dr.  Robert  Stanley,  for  stimulating  my  interest  in  this  problem 
and  for  providing  a dynamic  atmosphere  in  which  to  work;  to  Dr. 

Wa^Tie  Smith  for  his  counsel  and  to  him  and  his  wife.  Midge,  for 
their  warm  friendship  and  hospitality;  to  Ken  Strickland  for  his 
assistance  in  collecting  seeds  and  plant  material. 

I appreciate  the  financial  assistance  provided  by  the  U.  S. 
Forest  Service  and  the  added  encouragement  given  by  Dr.  Ray 
Brendemuehl . 

Lastly,  I thank  my  wife  and  sons  for  their  love  and  much  needed 
patient  understanding. 


11 


TABLE  OF  CONTENTS 


PAGE 

INTRODUCTION  1 

OBJECTIVES  3 

LITERATURE  REVIEW  6 

Mineral  Nutrition  of  Sand  Pine 7 

Photoassimilation  of  Carbon  Dioxide  8 

Concentration  8 

Light  Intensity 9 

Exposure  --  Length  and  Temperature  12 

Enzymes 14 

MATERIALS,  EQUIPMENT,  AND  METHODS  17 

Plant  Material 17 

Photoassimilation  Chamber  23 

Photoassimilation  of  ^"^C02 25 

Separation  of  Ethanol-Soluble  Components  

Measurement  of  Radioactivity  28 

Thin  Layer  Chromatography  29 

Sugars 29 

Organic  Acids  

Amino  Acids 

Radioautography  

Measurement  of  Enzyme  Activity  32 

i 


111 


TABLE  OF  CONTENTS 


CONTINUED 


PAGE 


Fructoaldolase 33 

Glyceraldehyde- 3- Phosphate  Dehydrogenase -NAD 
Dependent 33 

Phosphoglycerate  Kinase  33 

Glucose-6-Phosphate  Dehydrogenase  33 

6-Phosphogluconate  Dehydrogenase  35 

Acetone  Powders  --  Preparation  and  Protein  Extraction  . 37 

Preparation  of  Polyacrylamide  Gels  and  Electrophoresis  38 

Detection  of  Protein  and  Isoenzyme  Bands  39 

Proteins  and  Dehydrogenase  Isoenzymes  39 

Glucose-6-Phosphate  Dehydrogenase  and  Malate 
Dehydrogenase  . 40 

Sample  Size  and  Statistical  Analysis  41 

RESULTS  AND  DISCUSSION  43 

Photoassimilation  of  ^^CO.2 43 

Clarification  of  Extracts  and  Quenching  51 

Sugars 57 

Organic  Acids 65 

Am.ino  Acids 65 

Effect  of  Nutrient  Level  on  Seedling  Morphology  and  ^“^C 
Incorporation  67 

Color  and  Weight 67 

^'^C  Incorporation 70 

Biochemical  Pathways  Involved  75 

SUMMr.RY 94 

APPENDIX 97 

LITER.ATURE  CITED 107 


IV 


LIST  OF  TABLES 


TABLE  PAGE 

1 Source  and  concentration  of  elements  used 

in  the  complete  nutrient  solution  20 

2.  Chemical  and  physical  properties  of  soil  used 

to  raise  half-sibling  seedlings.  21 

3 Color  and  Rf  values  from  chromatograms  of 

known  sugars  used  to  identify  unknowns  30 

4 Distribution  of  photoassimilated  green 

sand  pine  seedling  tissue  56 

5 Seedling  weight  and  photoassimilated  ^^C 

distribution  in  response  to  nutrients  71 

6 Influence  of  N and  P fertilizer  on  the  distrib- 
ution of  weight  and  radioactivity  72 

7 Comparisons  of  the  soil  x tree  interaction  showing 
the  probability  of  a chance  occurrence  and  the 
soil  on  which  the  highest  values  were  obtained  go 

8 Distribution  of  half-sibling  seedlings 

possessing  3 to  7 cotyledons  87 

9 Protein  Rf  measurements  taken  from  half- 
sibling seedlings  grown  on  Lakeland  coarse 

sand  98 

10  Protein  Rf  measurements  taken  from  half- 

sibling  seedlings  grown  on  Paola  sand  101 

11  Protein  Rf  measurements  taken  from  parent 

trees  growing  at  their  original  locations  104 


I 


V 


LIST  OF  FIGURES 


FIGURE 

PAGE 

I 

Flow  chart  of  procedures  followed  in  part  I 

4 

2 

Flow  chart  of  procedures  followed  in  part  II 

5 

3 

Diagram  of  the  photoassimilation  chamber 

24 

4 

Reactions  for  measuring  fructoaldolase, 
glyceraldehyde-3-phosphate  dehydrogenase , 
and  3-phosphoglycerate  kinase 

34 

5 

Reactions  for  measuring  glucose-6-phosphate 
dehydrogenase  and  6-phosphogluconate 
dehydrogenase 

36 

6 

Distribution  of  radioactivity  in  seedlings 
allowed  to  photoassimilate  14c02 

44 

7 

Distribution  of  radioactivity  in  seedling 
tissues  exposed  to  14c02  in  the  light  and 
dark 

46 

8 

Quenching  curves  developed  to  compensate 
for  loss  of  counting  efficiency 

50 

9 

The  i4(]  incorporated  into  green  tissue 
of  Finus  clausa  in  response  to  different 
amounts  and  kinds  of  acid  used  to  release 
14c02  Kh14C03 

52 

10 

Comparison  of  clarifying  agents 

54 

11 

Chromatogram  showing  bands  of  standard 
and  unknown  sugars 

58 

12 

Radioautogram  of  a sugar  TLC  plate  (6 
weeks  exposure) 

59 

13 

Radioautogram  of  the  same  TLC  plate  used 
in  Figure  12  (2  weeks  exposure) 

60 

14 

Moribund  seedling  showing  constriction  near 
ground line 

63 

I 


LIST  OF  FIGURES  --  CONTINUED 


FIGURE 

PAGE 

15 

Organic  acid  TLC  plate 

66 

16 

Amino  acid  TLC  plate  for  fertilizer 
treatment  N2Pj^ 

68 

17 

Amino  acid  TLC  plate  for  fertilizer 
treatment  N2P2 

69 

18 

Seed  germination  from  superior  and  non- 
superior sand  pine  trees  at  5 locations 
designated  A to  E 

86 

vii 


Abstract  of  Dissertation  Presented  to  the 
Graduate  Council  of  the  University  of  Florida  in  Partial  Fulfillment 
of  the  Requirements  for  the  Degree  of  Doctor  of  Philosophy 

ENZYME  ACTIVITY  AS  AN  INDEX  OF  GROWTH  SUPERIORITY 
OF  PINUS  CLAUSA  VAR.  CLAUSA  ON  TWO  SOILS 

By 

Russell  MacBain  Burns 
August,  1971 

Chairman:  Dr.  William  L.  Pritchett 

Co-Chairman:  Dr.  Robert  G.  Stanley 

Major  Department:  Soil  Science 

Tliis  study  attempted  to  1)  identify  the  metabolic  pathways 

and  enzymes  involved  in  the  photos>mthetic  fixation  of  carbon 

and  to  determine  2)  if  metabolic  intermediates  were  altered  by 

changes  in  the  supply  of  nitrogen  and  phosphorus;  3)  if  activity 

level  of  specific  enzymes  differed  in  tissue  of  superior  and 

nonsuperior  trees  and  their  half-sibling  seedling  progeny; 

4)  if  the  activity  was  altered  by  the  soils  in  which  seedlings 

grew . 

Distribution  of  photoassimilated  ^^U02  measured  in  ethanol- 
soluble  fractions  of  green  tissue  from  3-month-old  Ocala  sand  pines 
grown  from  seed  in  sand  culture  and  complete  nutrient  solutions 
containing  two  levels  each  of  nitrogen  and  phosphorus.  Portions  of 
the  metabolic  pathways  involved  in  carbon  fixation  were  determined. 
Tlie  activity  and  electrophoretic  migration  rate  of  malate  dehydro- 
genase isoenz\nres,  glucose-6-phosphate  dehydrogenase  isoenzymes,  and 
proteins  were  compared  in  green  tissue  from  saw  log-size  superior 

viii 


and  neighboring,  nonsuperior  sand  pine  trees  and  their  half-sibling 
progeny  grown  in  pots  on  Lakeland  coarse  sand  and  Paola  sand. 

Sugars  contained  75%,  organic  acids  19%,  and  amino  acids  6%  of 
the  radioactive  carbon  in  the  ethanol -soluble  fraction  from  green 
tissue.  Radioactivity  was  highest  in  fructose,  glucose,  and  galactose. 
Nitrogen  directly  affected  chlorophyll  formation,  seedling  growth,  and 
photosynthetic  incorporation  of  14c.  Phosphorus  appeared  to  be  the 
principal  rate- limiting  element  in  the  incorporation  of  carbon  in 
sugars  and  in  some  organic  acid  precursors  of  amino  acids.  Results 
indicated  that  enzymes  of  glycolysis,  the  Calvin  cycle,  and  the 
tricarboxylic  acid  cycle  were  principally  involved  in  fixation  of 
carbon  in  sand  pine  seedlings  allowed  to  photoassimilate  ^^C02 
for  10  minutes  in  a controlled  environment. 

Measurements  of  activity  and  migration  of  isoenzymes  did  not 
provide  an  index  of  growth  superiority  in  parent  trees  or  in  half- 
sibling seedling  progeny.  Superior  parent  trees,  but  not  their 
progeny,  lacked  one  or  more  protein  bands  found  in  nonsuperior 
trees  indicating  that  a genetic  marker  exists.  However,  no  rela- 
tionship was  found  between  the  location  of  malate  dehydrogenase  and 
glucose-6-phophate  dehydrogenase  isoenzymes  and  protein  bands. 

Activity  and  Rf  values  of  some  malate  dehydrogenase  iso- 
enzyme and  protein  bands  were  altered  by  the  soil  in  which  seedlings 
grew  as  well  as  by  genetic  factors.  Both  the  isoenzyme  and  protein 
bands  and  factors  influencing  them  were  identifiable. 


ix 


INTRODUCTION 


Superior  trees  are  fast  growing  and  have  a desirable  morphology. 
They  are  sought  and  propogated  principally  to  shorten  the  rotation 
age  of  plantations,  i.e.,  the  time  needed  for  trees  to  reach 
merchantable  size.  Selection  of  superior  trees  is  based  primarily  on 
a comparison  between  the  candidate  and  neighboring  contemporaries  of 
the  same  species.  True  superiority  is  adjudged  by  the  ability  of 
grafted  stock  and  progeny  to  exhibit  the  same  superior  characteristics 
as  the  selected  candidate.  The  approach  is  sound  but  very  time 
consuming. 

A more  rapid  way  to  screen  candidate  superior  trees  may  be 
by  comparing  levels  of  enzymes  that  catalyze  growth  processes. 

Growth,  the  primary  index  of  superiority,  is  cumulative,  genetically 
controlled  (Squillace,  1965),  and  greater  in  superior  trees  than 
among  others  of  the  general  population.  Assimilation,  the  basic 
growth  process,  depends  upon  the  speed  of  certain  biochemical  reactions. 
Enzymes  control  the  rate  of  these  reactions  and,  thereby,  the  rate 
at  which  a tree  grows. 

Many  enzymes  are  involved  in  tree  growth.  This  study  measures 
activity  of  just  a few.  The  problems  are  to  select  for  assay  those 
enzymes  that  control  a biochemical  reaction  pathway  involved  in  the 
synthesis  of  anabolins,  which  most  differ  between  superior  and 
nonsuperior  trees,  to  determine  if  their  activity  is  influenced  by 


1 


2 


the  soil  in  which  the  pine  trees  grow,  and  to  determine  what  effect 
fertilization  with  phosphorus  (P)  and  nitrogen  (N)  has  on  photosynthetic 
fixation  of  carbon. 

Nutrient  levels  influence  rate  of  growth.  Sandy  soils  in  which 
sand  pines  grow  are  deficient  principally  in  P and  N (Brendemuehl , 

1967).  Sand  pines  respond  to  fertilization  with  these  elements. 

Ocala  sand  pine,  Pinus  olccusa  var.  clausa  Ward,  was  studied. 

It  is  native  to  droughty,  infertile  sandhill  soils  in  Florida  and  has 
become  increasingly  important  in  reforestation  of  these  difficult 
sites.  Superior  tree  selections  were  readily  available  for  seed 
collection  and  tissue  sampling. 


OBJECTIVES 


The  study  was  divided  into  twj  parts,  each  of  which  had  two 
objectives.  In  part  I,  experiments  were  designed  to  1)  identify 
the  metabolic  pathways  and  the  enzymes  involved  in  the  photo- 
synthetic fixation  of  carbon,  and  to  determine  2)  how  significantly 
these  pathways  might  be  altered  by  changes  in  the  supply  of 
plant  nutrients.  Figure  1 depicts  a flow  chart  of  procedures 
used  to  accomplish  these  objectives.  In  part  II,  objectives  were 
to  determine  3)  if  the  activity  level  of  specific  enzymes  differs 
in  tissue  of  superior  and  nonsuperior  trees  and  their  half-sibling 
progeny,  and  4)  if  the  activity  was  altered  by  the  soils  in  which 
seedlings  grew.  Figure  2 illustrates  the  procedures  followed  in 
the  second  part  of  the  study. 


4 


I COKPLFTE  NUTRIENT 

SOLUTION 

PLUS;  1 

POT 

POT 

Q 

1 SEEDLINGS 

ZTTTI 

_2 

Unr 


^^C02 

D 

ACHLOROPHYLLOUS 

TISSUE 

NEEDLES  AND 
GREEN  STEM 

u 

ETHANOL 

EXTRACTION 


SUGARS  I r> 


ORGANIC 

ACIDS 


D 


AMINO 

ACIDS 


D 


U D Q 

CHROMATOGRAPHIC 

SEPARATION 


RADIOAUTOGRAPHIC 
IDENTIFICATION  OF 
LABELED  COMPOUNDS 


LIQUID 

SCINTILLATION 
EQUIPMENT  TO 
MEASURE 
1^C02-FIXATI0N 


QUALITATIVE  AND 
QUANTITATIVE 
EFFECTS  OF  N AND  P 
FERTILIZATION 


Q 

IDENTIFICATION  OF  PRINCIPAL 
BIOCHEMICAL  PATHWAYS 
AND  ENZYMES 


TO 

PROTEINS  AND  ENZYMES 
IN  FIGURE  2 


Figure  1. — Flow  chart  of  procedures  followed  in  part  I 


5 


D 


D 


Ch 


Cl 


D 


D 


D 


D 


D 


D 


D 


D 


D 


D 


D 


D 


+-> 

!-< 

OS 

pH 


T5 

O 

s 

o 


o 

m 

w 

<1) 

p 

3 

0> 

u 

o 

p 

Ph 

4h 

O 

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u 

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s 

0 

1 
\ 


0 

g, 

•H 


2 

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rH 

M M 

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§ ^ 

O O 

5h  5 

« M 

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P>^  Uh 

Z M 

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a fa 

fa  z 

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O M 

LITERATURE  REVIEW 


Literature  pertinent  to  the  development  of  an  enzyme  index 
for  superior  trees  under  the  proposed  approach  encompasses  a wide 
variety  of  subjects  ranging  from  nutritional  requirements  for  sand 
pine  seedling  culture  to  methodology  for  enzyme  assay.  To  date  no 
one  has  published  results  of  an  approach  with  an  enzyme  assay. 

The  experiments  in  this  study  involve  a number  of  variables,  the 
effects  of  which  had  to  be  considered  in  sequence.  Factors  other 
than  those  to  be  tested  (constants)  had  to  be  maintained  within 
acceptable  limits,  or  at  desirable  levels,  in  order  to  determine 
accurately  the  effect  of  the  variable  under  consideration.  Pertinent 
literature  is  reviewed  in  those  sections  dealing  with  specific 
aspects  of  this  research,  so  that  it  will  be  in  context. 


6 


Mineral  Nutrition  of  Sand  Pine 


Similar  nutrient  solutions  were  employed  in  sand  and  water 
culture  (Hewitt,  1952;  Small  and  Leonard,  1969)  and  included  a 
wide  range  of  concentrations  of  macroelements  (Hacskaylo,  1962; 

Hoagland  and  Arnon,  1950)  . Tliis  suggested  that  each  species 
required  a particular  nutrient  regime  or  that  pines  exhibited  optimum 
growth  under  a diverse  range  of  nutrient  conditions.  This  was 
especially  true  of  N and  P. 

Published  (1967)  and  unpublished  work  by  Brendemuel.l  Indicated 
that  P.  clausa  growth  was  enhanced  by  N but  only  after  the  P deficiency 
inherent  in  infertile,  acid  sand  had  been  corrected.  Brendemuehl 
(personal  communication)  recommended  using  N and  P in  a ratio  of 
1 to  2 in  acid-washed  sand,  with  N supplied  at  the  rate  of  75  ppm. 

The  form  of  N used  also  affects  growth  and  protein  synthesis 
in  conifers.  Durzan  and  Steward  (1967)  grew  white  spruce  [Piaea 
glauca  (Moench.)  Voss]  and  jack  pine  {Pinus  banksiana  Lamb.) 
seedlings  for  478  days  in  sand  irrigated  with  nutrient  solutions 
containing  either  ammoniacal  nitrogen  (NH^-N)  or  nitrate  nitrogen 
(NO^-N) . The  fresh  weight  of  white  spruce  seedlings  was  greater  with 
NO^-N,  but  more  free,  non-protein  bound,  amino  acids  were  found  in 
seedlings  fed  NH^-N,  especially  in  stems  and  leaves.  Jack  pine 
seedlings  supplied  with  NH^-N  were  heavier  and  contained  more  total 
free  amino  acids  than  those  grov/n  with  NO^-N.  Because  free  amino 
acid  reserves  were  lowest  with  NO^-N,  Durzan  and  Steward  (1967) 


7 


8 


concluded  tliat  more  than  NH^-N  was  synthesized  into  proteins 

by  conifers,  '“.’ork  with  Southern  pines  (Barnes  and  Naylor,  1959; 
Barnes,  1962;  and  Pharis,  Bai'nes,  and  Naylor,  1964)  tended  to 
substantiate  this  conclusion. 

Photoass imi 1 ation  of  Carbon  Dioxide 

Concentration 

Ihe  average  concentration  of  CO2  in  the  atmosphere  is  about 
300  ppm  at  sea  level.  Of  this  amount  only  about  two-thirds  is 
available  for  photosynthesis  (Moss,  1962).  He  found  that  the  ability 
of  plants  to  utilize  CO^  varied  with  species.  Corn  (Zea  mays  L.), 
for  example,  has  a C02-compensation  point  of  less  than  10  ppm; 

Norway  maple  {Acer  ytatanoides  L.),  145  ppm.  Furthermore,  this 
equilibrium  between  CO^  production  and  utilization  varies  with  light 
intensity  and  temperature.  Moss  reported  that  in  a closed  system 
the  average  plant  reduces  CO^  concentration  to  a level  of  only 
50  to  100  ppm. 

At  best,  only  an  approximation  can  be  made  of  CO2  uptake  because 
photosynthesis  and  photorespiration  occur  simultaneously.  At  most 
light  intensities  much  of  the  CO2  respired  is  utilized  before  it  can 
diffuse  to  the  atmosphere.  Zelitch  and  Day  (1968),  working  with 
parent  and  mutant  progeny  of  tobacco  {Niootiana  tabacum  L.)  at 
several  concentrations  of  CO2  (including  CO^-free  air),  presented 
evidence  suggesting  that  the  increased  rate  of  CO2  uptake  in  hybrid 
plants  (higher  photosynthetic  efficiency)  may  be  attributed  to 
genetic  interference  with  the  photorespiratory  process,  i.e.,  net 
photosynthesis  was  high  because  photorespiration  was  lower  in  mutant 
siblings . 


9 


Growth  of  plants,  and  more  specifically  growth  of  pine  seedlings, 
will  occur  and,  in  fact,  will  be  enhanced  at  CO2  concentrations 
above  300  ppm.  Zelawski  and  Kinelska  (1967)  working  with  Scotch 
pine  (Firms  sylvestris  L.)  at  relatively  low  light  intensities 
(maximum  approximately  1,000  ft-c),  found  that  the  rate  of  photo- 
synthesis was  almost  directly  proportional  to  the  concentration  of 
CO2  within  the  range  of  200  to  400  ppm.  At  concentrations  above 
450  ppm  the  rate  of  photosynthesis  declined  and  approached  the 
point  where  the  response  to  increased  CO2  was  negligible  irrespective 
of  light  intensity.  Similar  findings  were  reported  by  Hughes  and 
Cockshull  (1969)  with  China  aster  (CaZVistephus  ohinensis')  at 
low  light  intensity.  Dry  matter  production  of  plants  grown  in  600  ppm 
CO2  was  slightly  higher  than  in  those  grown  at  900  ppm,  and  considerably 
higher  than  in  plants  grown  at  325  ppm.  The  natural  diffusion  gradient 
for  CO2  between  leaf  and  atmosphere  is  altered  at  high  concentrations 
and  may  cause  recycling  of  re5pired  CO2  at  higher  than  normal  rates. 
Extremely  high  CO2  concentrations,  2,000  to  4,000  ppm,  caused  stomata 
of  some  plants  to  close  (Pallas,  1965).  He  found  that  dicots  were 
more  tolerant  of  high  CO2  concentrations  than  monocots. 

Light  Intensity 

Uptake  of  CO2  is  affected  by  light  intensity.  Zelawski  and 
Kinelska  (1967)  presented  a graph  showing  that  the  shift  in  CO2 
compensation  point  with  varying  light  intensity  had  a parabolic 
configuration.  At  low  intensities  small  changes  induced  drastic 
shifts  in  the  CO2  compensation  point.  The  magnitude  of  the  shifts 
diminished  in  almost  exponential  fashion  as  light  intensity  approached 
47.5  and  100  % illumination  and,  although  intermediate  intensities  were 


10 

not  tested,  assumedly  at  intervening  intensities.  Unfortunately, 
light  saturation  was  not  attained  in  their  experiments. 

Light  saturation  was  reached  in  a study  of  eastern  hemlock 
{Tsuga  canadensis  L.)  in  Wisconsin  (Adams  and  Loucks,  1971).  Hemlock 
is  tolerant  of  dense  shade  and  develops  well  as  an  understory  plant. 
Illumination  of  foliage  at  midday  varied  between  25  and  500  ft-c  in 
the  forest.  Under  controlled  conditions  the  rate  of  net  photosynthesis 
increased  sharply  up  to  1,000  ft-c  and  then  began  to  decrease.  At 
3,000  and  3,500  ft-c  net  photosynthesis  was  approximately  the  same 
indicating  that  the  light  compensation  point  had  been  reached.  The 
data  suggested  that,  for  this  shade-tolerant  conifer,  changes  in 
intensity  above  1,000  ft-c  would  not  greatly  alter  CO2  uptake. 

Cooper  (1957)  reported  that  young  sand  pines  are  tolerant  of  shade. 

In  this  respect  the  two  conifers  are  alike. 

Keller  and  Koch  (1962)  examined  the  influence  of  mineral 
nutrition  upon  CO2  exchange  in  poplar  {Populus  euramerioana 
marilandiaa)  and  found  that  light  saturation  occurred  at  2,000 
ft-c  in  N-deficient  leaves.  Light  saturation  was  not  reached  at 
even  4,000  ft-c  in  "well-fed"  leaves.  However,  at  low  intensities 
of  up  to  500  ft-c  net  assimilation  was  the  same  in  N-deficient  and 
"well  fed"  leaves.  With  regard  to  the  dependence  of  net  photosynthesis 
upon  CO2  concentration  and  light  intensity,  their  findings  at  least 
partially  substantiated  those  of  Zelawski  and  Kinelska.  At  4,000  ft-c 
-the  CO2  uptake  of  poplar  leaves  was  strongly  influenced  by  foliar 
N content,  N-deficient  leaves  assimilated  only  60%  as  much  CO2 
as  normal  leaves,  were  proportionately  smaller  in  size,  and  contained 
only  55%  as  much  chlorophyll  per  unit  area.  There  was  a close 
correlation  between  the  chlorophyll  and  N content  of  poplar  leaves. 


11 


Light  intensity  influenced  NO^  uptake  and  the  subsequent  induction 
of  NO3  reductase  in  cereals  (Chen  and  Ries,  1969).  Rye  seedlings 
took  up  NO3  slowly  in  dark  and  rapidly  in  light.  After  a 12-hr 
exposure,  seedlings  subjected  to  about  300  ft-c  contained  as  much  NO3-N 
as  those  illuminated  with  800  to  1,5C0  ft-c,  suggesting  that  dependence 
of  NO3  reductase  activity  on  light  was  satisfied  at  the  lowest 
intensity.  Presumably  NO3  reductase  was  produced  in  the  dark.  Light 
and  prior  uptake  of  NO3  were  essential  for  the  induction  of  the 
enzyme.  Once  these  conditions  were  met  enzyme  production  continued 
to  increase  for  the  next  24  hours,  even  in  the  dark.  Within  the 
range  of  300  to  1,500  ft-c  induction  of  NO3  reductase  was  proportional 
to  light  intensity. 

Sand  pine  seedlings  appeared  to  be  umbraphilic  with  respect 
to  light  tolerance  and  juvenile  growth  (R.M.  Burns,  unpublished  data). 
Tests  conducted  in  an  experimental  nursery  support  the  observation; 
seedlings  raised  in  partial  shade  were  taller,  larger,  and  more 
verdant  than  those  grown  in  full  sunlight.  Results  suggested  that 
chlorophyll-catalyzed  photooxidation  induced  by  high  light  intensities, 
and  increased  respiration  in  response  to  high  summier  temperatures, 
as  noi'mally  encountered  on  exposed  sands,  contributed  to  slower 
growth  in  direct  sunlight. 

Meidner  (1970) , working  with  sun  and  shade  leaves  from  a 
variety  of  herbaceous  and  woody  plants,  noted  that  the  light  compen- 
sation point  was  most  closely  related  to  leaf  thickness,  lliinner 
shade  leaves  had  the  lowest  light  compensation  point.  Kramer  and 
Kozlowski  (1960)  made  a similar  observation  with  light  saturation 
of  sun  and  shade  leaves  of  European  beech.  Differences  in  saturation 


12 


levels  exist  because  higlier  intensities  are  needed  to  affect 
chlorophyll  molecules  deeply  imbedded  in  thick  leaves.  Pine 
needles  are  thicker  than  hardwood  leaves  and  much  less  efficient 
photosynthetically . Bonner  and  Galston  (1952)  reported  that  light 
saturation  of  pine  foliage  d^d  not  occur  even  at  intensities  approaching 
full  sunlight,  10,000  to  12,000  ft-c. 

Exposure  --  Length  and  Temperature 

Uptake  of  CO2  depends  upon  the  volume  involved,  the  amount  of 
chlorophyll  present,  the  rate  of  diffusion  inward,  and  the  rate  of 
photosynthesis,  llie  latter  is  temperature,  liglit,  and  CO2 
dependent.  Small  and  Leonard  (1969)  exposed  6-week-old  legumes 
in  plastic  bags  to  a volume  of  ^^C02  gas  with  radioactivity  of  5 
microcuries  (pc) . An  induction  period  of  15  min  in  direct  sunlight 
was  used.  No  mention  was  made  of  how  length  of  exposure  for  complete 
utilization  of  ^‘^C02  was  determined  but,  in  view  of  the  previously 
cited  work,  disposal  of  residual,  labelled  gas  obviously  was  necessary. 

Paired  leaves  on  intact  hybrid  and  parent  Mimulus  (Monkey 
flower)  plants  were  used  by  Decker  (1959)  to  measure  the  effect  of 
CO2  concentration  from  100  to  500  ppm  on  photosynthesis  at  temperatures 
of  20,  30,  and  40  C and  2,000  ft-c.  He  found  that  apparent  photo- 
synthesis increased  as  CO2  concentration  increased  and  temperature 
decreased.  Apparent  respiration  increased  with  temperature  but 
decreased  with  CO2  concentration.  The  CO2  compensation  point  increased 
almost  linearly  with  temperature.  Tlie  dependence  on  temperature 
was  ascribed  to  a temperature  coefficient  larger  for  respiration  than 
for  photosynthesis,  the  rate  of  respiration  being  more  than  3 times 
higher  in  light  than  in  darkness.  For  Mimulus,  at  least,  to  approach 


13 


the  CO^  compensation  point  with  the  shortest  possible  exposure 
time  at  a fixed' CO^  level  necessitates  use  of  a low  temperature. 

Dr.  W.  Zelawski  (personal  communication)  suggested  evolution  of 
14 

CO2  into  a closed  system  in  small  increments,  then  circulating 
the  gas  through  the  illuminated  chamber  for  2 hr.  This  procedure 
was  used  for  preliminary  work  because  it  provided  sufficient  time  for 
translocation  of  some  -labelled  products  to  the  roots  (Lister  et  al . , 
1968;  Small  and  Leonard,  1969)  and  insured  biochemical  fixation  of 
a large  volume  of  CO2  containing  sufficient  quantities  of  for 

detection. 

Devlin  (1968)  noted  that  an  optimum  rate  of  photosynthesis 
occurred  at  50  C during  Snort -term  exposure  and  at  22  C during 
long-term  e.xposure  of  Chlovella.  Nitssohia  closterium  reached 
an  optimum  rate  at  26  C and.  N.  palea  at  32  C at  high  light  intensities. 
Tlie  photosynthetic  rate  of  several  trees  and  seedlings  was  highest 
at  20-30  C (Kramer  and  Kozlowski,  1960).  Vose  and  Spencer  (1969) 
and  Zelawski  and  Kinelska  (1967)  reported  that  temperature  in 
closed  photoassimilation  chambers  usually  is  maintained  within  a 
range  of  20  to  27  C. 

The  effect  of  temperature  on  photosynthesis  and  respiration 
was  measured  using  sand  pine  (P.  clausa  var.  imw.ginata')  seedlings 
from  west  Florida  (Pharis  and  Woods,  1960).  Apparent  photosynthesis 
(mg.  CO2  taken  up  per  hr)  was  highest  at  23  C and  actual  photosynthesis 
(apparent  photosynthesis  + apparent  respiration,  as  mg.  CO., 
exchanged  per  hr)  was  equally  as  high  at  23  and  28  C.  This  was 
explained  by  the  fact  that  apparent  respiration  increased  with  tempera- 
ture throughout  the  range  tested  (18  to  48  C)  whereas  apparent 
photosynthesis  peaked  at  about  23  C. 


14 


Fnzymes 

Enzymes  are  proteins  that  catalyze  anabolic  or  catabolic 
reactions  along  biochemical  pathways.  The  net  result  is  growth  and 
reproduction.  Tlie  regulatory  mechanisms  for  protein  synthesis  and 
enzyme  activation  ai’e  not  fully  understood.  One  interesting  and 
widely  accepted  theory,  developed  through  intensive  experimentation  with 
microorganisms,  was  advanced  by  Jacob  and  Monod  (1961).  Although 
not  yet  verified  in  higher  plants  or  animals,  it  has  been  used  to 
explain  how  specific  enzymes  are  induced  and  why  rate  changes  occur 
during  development  and  maturation  of  higher  plants  (Borchert,  1967; 
Firenzuoli,  et  al . , 1968;  McClintock,  1961),  also  as  a basis  for  inter- 
preting the  genetic  implications  of  evolution  in  maize  (Efron,  1970)  and 
mutant  enzymes  (Sch.warcz,  1962),  photorespiration  in  tobacco 
(Zelitch  and  Day,  1968),  and  induction  of  NO^  reductase  in  rye  (Chen 
and  Ries,  1969). 

In  its  simplest  form  the  mechanism  involves  an  operon,  composed 
of  a structural  gene  and  an  operator  gene,  and  a regulator  gene. 

Activity  of  the  structural  gene  is  controlled  by  the  operator  gene. 

The  structural  gene  dictates  the  pattern  for  synthesis  of  a specific 
enzyme,  and  the  operator  gene  determines  the  rate  and  timing  of 
synthesis.  The  operon  may  be  activated  by  presence  of  exogenous 
substrate  and  external  conditions  to  induce  de  novo  S)oithesis  of 
specific  enz>Tne(s)  involved  in  the  sequential  metabolism,  of  the 


substrate . 


15 


The  regulatory  gene  determines  the  quantity  of  enzyme (s) 
produced.  It  produces  a specific  repressor  which,  when  activated  by 
metabolites,  acts  upon  the  operator  gene  to  block  the  mechanism 
of  the  operon.  Repression  may  be  influenced  by  a feed-back  control 
arising  from  the  accumulation  of  specific  catabolic  product?  in 
the  cytoplasm. 

Level  of  enzyme  activity  varies  during  plant  growth  (Borchert, 
1967),  during  the  advent  and  end  of  specific  physiological  processes 
(Chen,  Towill,  and  Loewenberg,  1970),  and  vvith  certain  changes  in 
environment  (Chen  and  Ries,  1969).  Exposure  of  seed  to  conditions 
conducive  to  germination  induces  changes  in  the  activity  level  of 
enzymes  involved  in  conversion  of  stored  food  to  energy  and  substrate 
necessary  for  assimilation  (Firenzuoli  et  al . , 1968).  Activity  may 
reach  a peak  in  a short  time  and  then  decline  as  the  substrate  is 
depleted  or  as  repressive  metabolites  are  produced  as  a feed- 
back control. 

External  conditions  that  influence  normal  growth  processes 
also  cause  change.  Sometimes  induction  of  enzyme  activity  is  under 
the  influence  of  more  than  one  external  factor.  Machlis  and 
Briggs  (1965)  report  that  day  length  as  well  as  temperature  may 
control  breaking  of  winter  dormancy  of  trees.  Premature  growth 
flushes  during  unseasonably  warm,  winter  weather  may  be  prevented  by 
a photo  control.  Chen  and  Ries  (1969)  found  that  light  as  vrell 
as  substrate  was  needed  to  induce  formation  of  NO^  reductase.  Light 
also  induced  changes  in  enzyme  activity  in  etiolated  bean  seedlings 
(Filner  and  Klein,  1968) . 


16 


llie  use  of  enzyme  activity  measurements  to  predict  the 
potential  for  rapid  growth  in  individual  plants  is  not  entirely 
new.  Hybrid  vigor  (heterosis)  in  maize  is  detectable  2 to  6 days 
after  germination  by  comparing  tlie  level  of  isocitric  dehydrogenase 
activity  of  hybridized  seedlings  with  that  of  progeny  of  inbred 
parent  plants  (Roos  and  Sarkissian,  1968).  Although  hybridization 
is  known  in  pine  the  study  material  was  not  hybridized. 

llie  rapid  growth  characteristic  of  superior  sand  pine  results 
from  a fortunate  combination  of  germ  plasm  which,  through  its 
sequential  control  of  enzyme  synthesis,  activity,  and  repression, 
governs  the  rate  of  its  physiological  processes.  The  hypothesis 
under  investigation  is  that  the  activity  of  biological  catalysts 
in  rapidly  growing,  superior  trees  differs  from  that  in  slower 
growing,  nonsuperior  pines. 

Because  of  the  great  number  of  enzymes  involved  in  plant  growth 
and  development,  some  system  or  method  usually  is  employed  to 
determine  the  one(s)  involved  in  particular  processes.  Roos  and 
Sarkissian  benefited  from  the  works  of  Gowan  (1952),  Hageman,  Leng, 
and  Dudley  (1966),  and  others  involved  in  the  heterotic  behavior 
and  breeding  of  corn.  In  nutritional  studies,  examination  can  be 
made  of  enzymes  containing  the  element  under  investigation.  Van 
Lear  and  Smith  (1970),  for  example,  examined  isoenzymes  of  poly- 
phenoloxidase,  peroxidase,  and  ascorbic  acid  oxidase  in  tissue 
of  pine  seedlings  grown  without  copper  or  without  iron  because 
these  enzymes  contain  copper  or  iron. 


M-XTERIALS,  EQUIPMENT,  AND  METHODS 
flant  Material 


Seeds  and  foliage  uere  collected  from  30  sand  pine  trees 
(P.  clausa  var.  clausa)  on  the  Ocala  National  Forest  in  Marion  and 
Putnam  Counties,  Florida.  Five  of  the  trees,  numbered  77,  82,  120, 

193,  and  199,  were  superior  selections  made  jointly  by  personnel  of 
the  Florida  Forest  Service,  U.  S.  Forest  Service,  St.  Regis  Paper 
Company,  and  the  Forest  Physiology  and  Genetics  Laboratory  of  the 
University  of  Florida.  Within  100  feet  of  each  superior  tree  5 non- 
superior trees  of  similar  age  were  selected  as  representatives  of 
the  general  population  growing  under  conditions  similar  to  the 
superior  tree. 

Cones  of  the  1967  seed  crop  were  collected  from  the  30  trees. 

Ihey  were  opened  in  a force-draft  oven  at  60-63  C and  the  extracted 
seeds  were  stored  at  temperatures  below  5 C.  Needle  samples  from 
parent  trees  were  collected  and  used  during  the  summer  of  1970.  Needles 
were  placed  in  plastic  bags,  quick-frozen  in  liquid  N'2,  transported 
to  the  laboratory  on  dry  ice,  and  stored  at  -20  C until  used. 

Seeds  composited  from  nonsuperior  pines  were  used  throughout  the 
first  series  of  experiments.  On  April  21,  1968,  they  were  surface 
sterilized  with  sodium  hypochlorite  and  planted  in  S polyethylene- 
lined  pots,  each  filled  with  approximately  27  pounds  of  dried,  acid- 
washed  sand.  Pots  were  cylindrical,  measured  21  cm  in  diameter  and 
height,  and  were  made  with  a 25-mjn  diameter  hole  through  the  side  at 


17 


18 


the  bottom.  A one-hole  stopper  masked  with  glass  wool  was  fitted 
in  the  hole  to  provide  for  irrigation  and  drainage  without  loss  of 
soil.  Fifty  seeds  were  planted  in  each  pot.  Distilled  water  and 
subirrigation  were  used  to  germinate  t’le  seeds.  They  were  allowed 
to  germinate  for  30  days  and  were  then  thinned  to  25  per  pot. 
lliose  that  germinated  later  were  discarded. 

Seedlings  were  raised  under  greenhouse  conditions  using 
complete  nutrient  solutions  patterned  after  those  of  Hacskaylo 
(1962).  Solutions  contained  either  7.5  ppm  (Nj^)  or  75.0  ppm  (N2) 
of  N and  either  15.0  ppm  (Pi)  or  150.0  ppm  (P2)  of  P (Table  1). 
Seedlings  in  2 pots  were  supplied  with  one  of  the  4 solutions 
(N^Pj^j  ^iP2j  '^’2^1’  ^^2^2^  twice  weekly  throughout  the  fi  'st  series 

of  experiments. 

Seedlings  and  soil  from  one  pot  of  each  fertilizer  treatment 
were  transferred  to  tubules  on  June  19,  1968.  Tubules  were  15  cm 
long,  2.5  cm  in  diameter,  and  were  constructed  from  rigid  polyvinyl 
chloride  (PVC)  water  pipe.  ITiey  were  fitted  with  a one-hole 
neoprene  stopper  masked  with  glass  wool  to  permit  irrigation  and 
drainage  yet  prevent  loss  of  sand.  Subirrigation  and  immediate 
drainage  were  used  to  feed  seedlings  and  promote  soil  aeration  in 
pots  and  tubules.  To  prevent  accumulation  of  nutrient  salts, 
seedling  containers  were  flushed  with  deionized  water  at  biweekly 
intervals . 

Seeds  from  superior  and  nonsuperior  trees  were  used  in  the  second 
series  of  experim.ents . On  December  1,  1969,  50  seeds  from  each 
tree  v.-ere  planted  in  each  of  two  polyethylene- lined  greenhouse 
pots  previously  described.  One  pot  contained  a Lakeland  coarse  sand 
from  Calhouii  County  and  the  other  a Paola  sand  from  Marion  County, 


19 


Florida.  These  soils  were  used  because  within  the  limited,  natural 
range  of  sand  pine  they,  and  their  respective  hyperthermic  and 
thermic  counterparts,  Astatula  and  Lakewood  sands,  comprise  a 
major  portion  of  the  sandhill  sites  upon  which  the  species  grows. 

Each  contained  7.5  cm  of  topsoil  (A^  horizon)  and  about  12.5  cm  of 
soil  from  an  underlying  horizon  (C  for  Lakeland  and  A2  for  Paola) . 

Procedures  outlined  by  Jackson  (1958)  and  by  the  American 
Society  of  Agronomy  and  American  Society  for  Testing  and  Materials 
(1965)  were  used  to  analyze  soils.  Soil  pH  was  measured  using  a 
1 to  5 soil-water  suspension  and  a glass  electrode.  Cation  exchange 
capacity  was  determined  using  normal  neutral  ammonium  acetate. 
Available  nutrients  were  extracted  from  the  soil  with  ammonium 
acetate  buffered  at  pH  4.8.  The  concentration  of  individual  elements 
in  solution  was  measured  using  the  equipment  or  procedures  that  follow: 
Ca  and  Mg  with  a Beckman  Model  DU  flame  spectrophotometer;  K with 
a Beckman  Model  B flame  spectrophotometer;  P using  the  ch loros tannous- 
reduced  molydophosphoric  blue  color  method  in  a sulfuric  acid  system 
with  a Spectronic  20  colorimeter;  and  A1  with  a Perkin-Elmer  model 
303  atomic  absorption  spectrophotometer.  Organic  matter  was 
determined  using  the  Walkley-Black  chromic  acid  oxidation  procedure. 

The  modified  Kjeldahl  method  was  used  to  determine  total  N. 

Particle  size  distribution  was  determined  using  the  hydrometer 
method,  and  sand  fractions  were  separated  by  dry  sieving.  Soil 
moisture  at  15  and  1/3  atmospheres  was  measured  using  pressure  plate 
apparatus.  Physical  and  chemical  analyses  of  these  soils  are 
summarized  in  Table  2. 


20 


Table  1, --Source  and  concentration 


nutrient  solution 

Nutrient 

element 

Source 

N 

NH4OH  and  HNO3 

P 

H3PO4 

K 

KOH 

Ca 

CaCl2*  2H2O 

Mg 

MgSO^ • 7H2O 

S 

MgS04 • 7H2O 

B 

H3BO3 

Mn 

MnCl2'4H20 

Zn 

ZnCl2 

Cu 

CuCl2‘2H20 

Mo 

H2Mo04-H20 

Fe 

Fe  - EDTA 

of  elements  used  in  the  complete 


Nutrient  Solution* 

NiPi 

N1P2 

N2P1 

N2P2 

7.5 

7.5 

75.0 

75.0 

15.0 

150.0 

15.0 

150.0 

200.0 

200.0 

200.0 

200.0 

100.0* 

100.0 

100.0 

100.0 

50.0 

50.0 

50.0 

50.0 

65.9 

65.9 

65.9 

65.9 

0.4 

0.4 

0.4 

0.4 

0.04 

0.04 

0.04 

0.04 

0.05 

0.05 

0.05 

0.05 

0.02 

0.02 

0.02 

0.02 

0.03 

0.03 

0.03 

0.03 

5.00 

5.00 

5.00 

5.00 

*Solutions  were  adjusted  to  pH  5.85  with  HCl  or  NaOH 


Table  2. — Chemical  and  physical  properties  of  soil  used  to  raise  half-sibling  seedlings 


21 


CN 

1 

\0 

1 

CN 

1 

1 

^ 1 

O 

1 

o 

1 

2:  1 

1 

• 

1 

r- 

■p 

o 

1 

o 

1 

CJ 

r-* 

•H 

s 

x: 

o 

p 

o 

to  Pv  CM 

1 

1 

a. 

CO 

1 

rH 

1 

O 1 

1 

• 

1 

5h 

I-H 

I 

rH 

1 

O 

+-> 

LO 

LO 

lO 

LO 

P( 

--H  1 

• 

• 

0 

< 1 

rH 

00 

to 

o 

1 

LO 

X 

1 

1 

0 

1 

lA 

1 

G 

1 

O 

1 

»H 

75  ! 

1 — 

LO 

P 

p 1 

i-H 

fH 

o3 

C 1 

P 

Q 1 

•H 

•H  1 

s 

P 1 

p 

P 1 

o 

1 

CN 

LO 

CN 

p 

2:  e 

• 

Q) 

O-  Ph  O 

CN 

o 

o 

0)  Cl. 

75 

t-H  1 

O 

O 

rCt  1 

•tH 

75 

1 

p 

»-H  1 

o 

O 

P 

•H  1 

o 

O 

O 

cj  bO  1 

cj 

c3 

o 

(N 

c 

> :s  I 

u 

P 

rH 

o 

< 

< I 

C-H 

H 

p 

1 

o 

1 

rC 

cj 

1 

Ph 

o 

1 

o 

♦H 

1 

p 

1 

p 

<D 

1 

CN 

LO 

LO 

o 

a \ 

vO 

CN 

rH 

o 

U 

U I 

p. 

CO 

bo 


O 


o 


o 

o 

00 

•H 

CN  O 

to  1 

rH  1 

P 

U .-1 

• 1 

• 1 

O 

ly  \ 

to  I 

CN  1 

ctJ 

U • 

P 

LO 

vO 

\o 

LO 

lO 

LO 

2: 

o 


ai 

O 


CM 


< 


P 

o5 

tXi 

ci 

rH 

i-A 

i-H 

0) 

o 

o 

Pi 

CO 

cj 

o3 

P 

-4 

u 


X 

O 

• 

*T3 

o 

00 

rC 

• 

P 

o 

e 

• 

n: 

"O 

p 

p 

o 

o 

• 

•H 

P 

o 

u 

P 

0 

• 

OJ 

*H 

rj 

s 

cd 

P 

P 

o 

p 

P 

P 

Pi 

p: 

0) 

0 

P 

u 

p 

o 

s 

o3 

0 

tH 

7) 

rH 

C3 

P 

ca 

c; 

o 

1 

rH 

3 

rH 

X 

x: 

•H 

o 

•H 

0 

P 

o 

P 

t-A 

O 

O 

Pi 

rH 

S 

75 

s 

fH 

0 

s 

c3 

< 

rH 

CN 

to 

tt 

Table  2.--  Continued 


22 


•M 

c 

to 

1 

f-H 

LO 

vO 

vO 

0) 

to 

1 

(N 

i-H 

to 

+-> 

0 

1 

• 

c 

o 

u 

o 

u 

fn 

O 

rC 

Ph 

to 

o 

1 

1 

1 

to 

CM 

CM 

3 

E 

t-H 

00 

4-> 

4-> 

vO 

CM 

to 

V) 

LO 

< 

• 

•H 

o 

S 

1-H 

rH 

O 

CM 

i-H 

X 

cS 


to 

to 


w 

(U 

to 


c 

< 


nj 

U 


t/i 

X 

a, 


+J 

1 

LO 

o 

to 

00 

1 

• 

• 

•H 

1 

CM 

I-H 

CM 

CO 

1 

P 

lO 

c 

c 

o 

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23 


Seeds  were  germinated  and  seedlings  grovm  using  distilled 
water  and  subirrigation.  Approximately  45  days  after  planting, 
seedlings  were  thinned  to  25  per  pot.  On  August  25,  1970,  needles 
and  green  stems  were  harvested,  quick  frozen  in  liquid  N2,  then  stored 
at  -20  C until  needed. 

Photoassimilation  Chamber 

A chamber  for  photosynthetic  fixation  of  CO2  in  pine  seedlings 
was  designed  and  built  specifically  for  this  project.  It  was 
constructed  entirely  of  plexiglass  and  consisted  of  a cubic 
chamber,  with  dimensions  of  30.5  cm,  surrounded  on  5 sides  by  a 
10- cm  water  jacket.  Figure  3.  Access  to  the  chamber  was  provided 
through  a gas-tight  bottom  board. 

Tne  environment  of  the  chamber  was  controlled.  Constant 
light  intensity  of  2,000  ft-c  was  provided  by  two  overhead,  narrow- 
spot  Sylvania  cool-lux  lamps  (P.4R  300/2NSP)  . Temperature  was 
maintained  at  25  ^ 1 C with  ice-cooled  water  piped  through  the 
water  jacket.  Air  and  introduced  CO^  were  circulated  through  a closed 
system  at  9 to  10  ft  per  hr  by  a sealed  pump.  Even  distribution 
of  gases  within  the  chamber  was  assured  by  a magnetically  driven 
fan.  Gases  entered  the  chamber  through  the  base  of  the  fan 
and  left  via  4 e.xhaust  ports  in  the  bottom  board.  Tests  with 
smoke  showed  that  circulation  within  the  chamber  was  good  and 
that  no  leakage  occurred. 

Two  CO^  traps  and  an  air  drier  supplemented  the  closed 
system.  The  drier  (sulfuric  acid  solution  of  density  1.40) 
maintained  a relative  humidity  of  37%  in  the  air  bubbled  through 
it.  CO2  traps  containing  a 20%  solution  of  KOH  were  used  to 


24 


Figure  3. --Diagram  of  the  photoassimilation  chamber  (A)  and  components  of  the  closed  system: 
dehumidifier  (B) , 2 CO2  traps  (C) , CO-  generator  (D) , Pump  (E) , magnetic-driven 
fan  (F),  magnetic  stirrer  (G) , removable  bottom  board  (H) , intubuled  seedlings  (J) , 
heat  screen  (K) , and  adjustable  lights  (L) 


25 


cleanse  the  system  of  CO2  and  14c02.  Traps  were  bypassed  wlien 
was  added  to  the  system. 

1 A • 

CO2  and  ■"  CO 2 was  generated  by  injection  of  10  ml 

concentrated  H2S0^  into  a 5 ml  aliquot  of  XHCO3  and  KH^'^CO^. 

Ba^^^CO^  with  a specifit.  ac■^ivity  of  39.2  x 10^  pc/mM 
was  used  as  the  source  of  14c02.  To  provide  the  20  yc  of 
activity  and  500  ppm  of  CO2  needed  for  each  replicated  run  in 
the  photoassimilation  chamber  required  0.10065  mg  of  Bal^^o^ 
and  124.6313  mg  of  BaC03.  Because  of  difficulty  in  weighing  such 
minute  quantities  of  Bal^co^,  an  alternate  procedure  was  devised 
to  insure  accurate  replication.  CO2  and  ^'^C02  were  evolved  from 
sufficient  BaCO^  and  Bal4c03  for  20  replications  (2.0130  mg 
Bal^co^  and  2.493  g BaC03)  in  a closed  system  using  2 equivalents 
of  lactic  acid.  Gases  were  trapped  in  a solution  containing 
an  excess  of  KOH  (1.5  g in  100  ml  of  boiled,  glass  distilled 
water).  A 5.0  ml  aliquot  registered  4.5  x 10^  counts  per  min 
(cprn)  on  liquid  scintillation  equipment  (101%  of  the  activity 
calculated  to  be  in  a sample  containing  20  yc  of  activity). 

Photoassimilation  of  14c02 

Seedlings  were  sealed  in  their  tubules  with  parafilm  and 
liquid  latex  to  prevent  uptake  of  by  roots  (Stemmet, 

DeBruyn,  and  Zeeman,  1962;  Fadeel,  1963)  and  microorganisms  in 
the  soil.  Seedlings  representing  each  fertilizer  regime  were 
treated  simultaneously.  Tliey  were  preconditioned  to  the  temperature, 
humidity,  and  light  intensity  of  the  chamber  for  20  min  while 
atm.ospheric  COg  was  trapped.  Preconditioning  in  light  enables 


26 


plants  "...to  generate  any  reducing  agents  active  in  photosynthesis" 
or  "...to  deplete  any  reducing  agents"  in  darkness  (Stutz  and 
Burris,  1951).  After  preconditioning,  500  ppm  of  CO2  containing 
20  pc  activity  v;as  released  into  the  circulating  air  of  the 
system  from  Klll^cOg  and  WICC^,  I’sing  excess  acid.  At  the  conclusion 
of  the  photoassimilaticn  period  residual  was  trapped. 

Tubules  were  removed  from  tlie  chamber  and  plunged  into  ice 
vvater.  Seedlings  were  washed  free  of  sand,  blotted  dry,  and 
placed  in  individually  tared  and  labelled  plastic  bags.  Bags 
were  sealed  after  evacuating  the  air  and  then  plunged  into  liquid 
^2'  Frozen  seedlings  were  stored  at  -20  C until  seedlings  were 
partitioned  and  weighed. 

Low  temperatures  were  maintained  during  weighing.  Bags  containing 
seedlings  were  blotted  dry  of  condensation  and  weighed  on  a Mettler 
balance.  Seedlings  were  removed  and  divided  into:  1)  epicotyl 

(needles  and  chlorophyllous  stem),  2)  nonchlorophyllous  stem 
(hypocotyl),  and  3)  roots;  then  (1)  and  (2)  were  weighed; 
weight  of  3 was  obtained  by  subtraction.  Seedling  parts  were 
returned  to  the  bag  and  stored  at  -20  C before  making  ethanol 
extracts . 

Ethanol -soluble  extracts  were  made  of  weighed  seedling  parts. 
Needles  and  green  stem,  nongreen  stem,  and  roots  were  individually 
ground  with  a cold  mortar  and  pestle  using  liquid  N2,  washed  into 
Ehrlenmeyer  flasks  with  liquid  N2  and  95%  ethanol,  and  boiled  for 
10  min.  Cooled  extract  was  vacuum  filtered  into  scintillation 
flasks.  Residues  were  discarded. 


27 


Separation  of  Ethanol -Soluble  Comporients 

Extracts  were  evaporated  just  to  dryness  in  a pan  of  warm 
sand  (80-90  C) , cooled,  and  the  residue  taken  up  in  5 ml  of  15% 
ethanol.  Four  ml  were  fractionated  into  sugars,  amino  acids, 
and  organic  acids  using  ion-exchange  resins.  The  remaining  1 ml 
was  retained  to  sample  radioactivity  of  the  extract. 

Procedures  for  fractionation  of  ethanol  extracts  on  ion 
exchange  columns  were  those  of  Shiroya  et  al.  (1962,  1966) 
modified  by  Riech  (1970) . The  extract  was  pipetted,  a drop  at 
a time,  directly  onto  two  seriate  resin  columns  each  5 cm  long 
X 1 cm  diameter.  The  first  contained  50-100  mesh  Dowex  1-x  8 
resin  converted  from  the  Cl"  to  HCOO"  form  with  formic  acid,  and 
the  second  contained  200-400  mesh  Dowex  50W-x  8 in  the  H+  form. 
The  extract  was  washed  through  both  columns  with  150  ml  of  glass- 
distilled,  deionized  water  added  at  the  rate  of  30  to  40  drops 
per  min.  The  elution  contained  sugars.  Amino  acids  were 
elutriated  from  the  50W-x  8 resin  column  with  70  ml  of  2N  NH4OH, 
and  organic  acids  from  the  1-x  8 column  with  70  ml  of  5N  formic 
acid.  Using  this  procedure  in  control  experiments,  Riech  reported 
98%  recovery  of  glucose-14c  in  the  sugar  fraction,  91%  recovery 
of  Leucine- in  the  amino  acid  fraction,  and  98%  recovery  of 
orotic  acid-^'^C  in  the  organic  acid  fraction. 

Eluted  fractions  were  evaporated  to  dryness  (80-90  C) 
and  taken  up  in  6 ml  of  10%  ethanol.  Half  (3  ml)  of  each  fraction 
was  reserved  for  further  separation  by  thin  layer  chromatography; 
the  remainder,  and  the  1 ml  sample  of  ethanol  extract,  were  used 
to  obtain  measurements  of  radioactivity. 


28 


Riech  (1970)  suspected  that  heating  extracts  on  a hot 
plate  to  SO  or  90  C might  cause  loss  of  some  of  the  moi'e  volatile 
amino  and  organic  acids  and  modified  his  technique  for  concentrating 
extracts.  The  modified  technique  was  not  used  because  plant 
tissue  was  boiled  in  95%  ethanol  to  prepare  the  extract. 

Volatile  acids  do  not  survive  the  preparatory  steps  (Ting  and 
Dugger,  1965).  Vacuum  evaporation  and  lyophilization  were  used 
to  concentrate  small  volumes,  but  both  procedures  were  excessively 
time-consuming  and  neither  proffered  special  advantages,  so  the 
practice  was  abandoned. 

Organic  acids  did  not  rcdissolve  well  in  the  diethyl  ether 
used  to  remove  impurities.  Water  or  ethanol  were  substituted  and 
found  to  give  better  resolution.  Because  it  evaporated  more  rapidly 
during  spotting  of  plates,  80%  ethanol  was  used. 

Measurement  of  Radioactivity 

Samples  of  ethanol  extract,  sugars,  amino  acids,  and  organic 
acids  were  evaporated  to  dryness  (80-90  C) . The  residue, 
dissolved  in  0.5  ml  absolute  ethanol,  was  taken  up  in  10  ml  of 
scintillation  fluid  (BBOT)^,  and  the  radioactivity  counted  for  5 min. 
Counts  of  radioactivity  were  measured  using  Model  3380  Packard 


BBOT  is  2,5-bis  [2- (5-tert-Butylbenoxazolyl) ] thiophene  and 
the  scintillation  fluid  or  "cocktail"  consisted  of  4 grams  of  BBOT 
dissolved  in  1 liter  certified  grade  toluene. 


29 


Tri-Caib  liquid  scintillators,  units  were  normalized,  and  internal 
standards  used. 

Tliin  Layer  Cliromatography 

Sugars,  organic  acids,  and  amino  acids  were  separated  into 
component  parts  by  thin  layer  chrv.matography  (TLC)  . Commercially 
available  plates  were  used.  For  sugars  and  organic  acids 
separations  were  made  in  one  direction  on  glass  plates  coated 
with  silica  gel.  Two-dimensional  separation  on  cellulose-coated 
acetate  plates  was  used  for  amino  acids. 

Sugars 

Plates  were  scored  vertically  so  as  to  contain  spots  and 
convert  them  to  bands  (Stahl,  1969).  Each  was  spotted  with 
unknown  sugar  solution  and  with  solutions  of  known  sugai's.  Tests 
showed  tliat  the  clearest  bands  and  best  definition  were  obtained 
with  40  to  50  pi  of  unknown  sugar  solution  per  spot. 

Sugars  were  separated  by  processing  the  plates  twice  with  a 
solvent  composed  of  n-propanol,  ethyl  acetate,  and  water  (6:3:1). 
Plates  were  completely  dried  in  a fume  hood  each  time  the  solvent 
front  reached  the  upper  edge.  Bands  were  detected  and  colors 
developed  by  gradually  heating  plates  sprayed  with  a mixture  of 
anisidine  hydrocliloricie,  aniline  diphenylamine,  and  phosphoric  acid 
(5:5:1)  from  27  to  36  C in  a force-draft  oven  over  a period  of 
from  5 to  10  min  (Lewis  and  Smith,  1969  as  modified  by  Riech, 

1970) . Sugars  were  identified  using  a combination  of  colors  and 
Rf^  values  from  samples  of  known  sugars.  Table  3. 


_ Distance  compound  moved 
Distance  solvent  moved 


30 


Table  3. --Color  and  Rf-values  from  chromatograms  of  knou-n  sugars 
used  to  identify  unknowns 


Sugars 

Molecular 

Weight 

No.  of 
Carbon 
Atoms 

Raffinose 

594.5 

18 

Sucrose 

342.3 

12 

Galactose 

180.2 

6 

Glucose 

180.2 

6 

Fructose 

180.2 

6 

Mannose 

180.2 

6 

Arabinose 

150.1 

. 5 

Ribose 

150.1 

5 

Xylose 

150.1 

5 

Color 

Range  of 
Rf 

Non-Descriptive 

.04-. 06 

Brov^{nish -yellow 

.12-. 15 

Brown 

.12-. 15 

Brown 

.15-. 18 

Yellow 

.16-. 19 

Brownish-yellow 

.17-. 21 

Brownish-blue 

.18-. 21 

Non-Descriptive 

.21-. 25 

Non-Descriptive 

.24-. 27 

1 


31 


Organic  Acids 

Preliminary  tests  showed  that  the  quantity  of  organic  acids 
in  green  tissue  was  low  and  that  separation  of  the  unknowns  was 
difficult.  Spots  made  from  40  to  SO  yl  of  solution  required  4 
separate  processing  treatments  with  water-saturated  ethyl  3thfr- 
formic  acid  (7:1)  to  obtain  discernible  separation  into  distinct 
bands  (Ting  and  Dugger,  1965).  The  bands  stained  yellow  against 
a blue  background  when  air-dried  plates  were  sprayed  with  a 
tincture  of  bromcresol  green  (0.04  g bromcresol  green  in  100  ml 
95%  ethanol,  then  0.1^  NaOH  was  added  drop  by  drop  until  a blue 
coloration  appeared)  (Krebs,  Ileusser,  and  U'immer,  1969). 

Amino  Acids 

Soltanabadi ' s (1966)  procedure  was  used  for  the  two-dimensional 
separation  of  amino  acids  on  cellulose-coated  acetate  plates. 

Spots  were  separated  in  the  first  dimension  using  a solvent 
composed  of  2-propanol,  formic  acid,  and  water  (40:2:10),  and, 
after  drying,  were  separated  in  the  second  dimension  with 
tertbutanol,  methyl  ethyl  ketone,  3%  NH4OH,  and  water  (50:30:10:10). 
Spots  were  developed  on  thoroughly  air-dried  plates  with  ninhydrin 
spray  (0.5  g ninhydrin  in  100  ml  acetone)  and  heat  (65  C for  30 
min) . 

Radioautography 

Counts  of  radioactivity  using  liquid  scintillation  equipment 
provided  a quantitative  measure  of  photoassimi lated  in 
ethanol  soluble  fractions  of  plant  parts,  i.e.,  sugars,  organic 
acids,  and  amino  acids.  Radioautography  was  used  to  obtain  a 
comparative  measure  of  radioactivity  in  individual  compounds 


32 


separated  and  identified  by  TLC.  Films  were  exposed  to  the  TLC 

plates  for  2 weeks  or  6 weeks;  exposure  for  6 weeks  recorded  the 

relative  concentration  of  in  all  compounds.  At  2 weeks  only 

the  most  radioactive  compounds  exposed  the  film.  ' Although  methods 

are  available  for  more  quantitative  i.ieasurements  of  photoassimilatcd 
14 

C,  radioautography  served  the  purpose  of  this  study,  i.e.,  to 
identify  those  compounds  incorporating  the  most  ^‘^C. 

Measurement  of  Enzyme  Activity 

Needles  and  green  stems  were  homogenized  in  a Sorvall  Omni- 
mixer with  a 2-fold  weight  of  extracting  solution  (10  mM  2- 
mercaptoethanol , 2 mM  F.DTA,  100  itlM  phosphate  buffer,  pH  7.2)  for 
1 min  at  -15  C.  Tlie  brei  wa‘=  extracted  for  60  min  at  0 C with 
magnetic  stirring.  Tlie  insoluble  fraction  was  sedimented  by 
centrifugation  at  37,000  x g for  10  min  at  4 C,  then  the  supernatant 
was  centrifuged  at  100,000  x g for  30  min  at  0 C.  Clear  supernatant 
was  used  for  detei'mination  of  enzyme  activity. 

Tne  activity  of  three  enzymes  of  glycolysis:  fructose 

diphosphate  aldolase  (EC  4.1.2.13),  glyceraldehyde-3-phosphate 
dehydrogenase-NAD  dependent  (EC  1.2.1.12),  and  3-phosphoglycerate 
kinase  (2. 7. 2. 3),  and  two  enzymes  of  the  pentose  phosphate  shunt: 
glucose-6-phosphate  dehydrogenase  (EC  1.1.1.49)  and  6-phosphogluconate 
dehydrogenase  (EC  1.1.1.44)  were  measured  using  optical  tests 
based  on  the  extinction  coefficient  of  pyridine  nucleotide 
coenzymes  at  -340  my  and  a Beckman  model  DB  spectrophotometer  with 
a Sargent  recorder.  Procedures  were  those  employed  by  Firenzuoli 
et  al.  (1967)  but  were  modified  for  use  on  the  Beckman  spectro- 
photometer. Extinction  was  measured  at  a wavelength  of  340 
my  instead  of  366  my. 


33 


Fructoaldolase 

Measurement  of  fructoaldolase  activity  involved  a coupled 
reaction  (Figure  4)  with  two  accessory  enzymes  (triose  isoraerase 
and  glycerol-3-phosphate  dehydrogenase).  Ihe  reaction  mixture 
contained:  50  mM  triethanolamine  hydrochloride  (TRA-HCl)  buffer, 

5 mM  EDTA,  0.15  mM  nicotinamide  adenine  dinucleotide-reduced 
form  (NADH),  4 mM  fructose-1,  6-diphosphate,  0.72  lU  per  ml  glycerol- 
3-phosphate  deliydrogenase,  0.72  lU  per  ml  triosephosphate  isomerase, 
and  green  tissue  extract.  Tlie  product  of  the  reaction  was 
glycerophosphate . 

Glyceraldehydc-3- Phosphate  Dehydrogenase-NAD  Dependent 

One  accessory  enzyme  (phosphoglycerate  kinase)  was  used  in 
the  coupled  reaction,  depicted  in  Figure  4.  The  reaction  mixture 
included:  50  imM  TFL\-HC1,  5 mM  EDTA,  0.15  mM  NADH,  1.5  mM  adenosine 

triphosphate  (.^TP) , 3.3  mM  MgS04,  10  mM  cysteine-hydrochloride, 

7 mM  3-phosphoglycerate,  1.8  iU  per  ml  phosphoglycerate  kinase,  and 
extract.  Tlie  product  of  the  reaction  was  glyceraldehyde-3-phosphate , 
Phosphog lycerate  Ki nase 

This  is  the  same  reaction  as  that  used  for  glyceraldehyde-3- 
phosphate  dehydrogenase  reversed.  The  reaction  mixture  was  identical 
except  that  0.9  IU  per  ml  glyceraldehyde-3-pliosphate  dehydrogenase 
substituted  for  3-phosphoglycerate  kinase.  The  product  was  3- 
phosphoglycerate . 

Glucose- 6 -Phosphate  Dehydrogenase 

Tlie  reaction  mixture  contained  50  mM  1R,'\-HC1  (pH  7.6), 

5 mM  EDTA,  0.5  mM  NADP,  1.8  mM  glucose-6-phosphate,  and  extract. 

The  product  was  gluconoiactcne-5-phosphate  (Conn  and  Stiimpf, 

1964).  In  aqueous  solution  containing  the  obligatory  metal  ion 


FRUCTOALDOLASE 


34 


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Figure  4.  Reactions  for  measuring  fructoaldolase,  glyceraldehyde-3-phosphate  dehydrogenase,  and 
3-phosphoglycerate  kinase 


35 


cofactor  Mg++  the  reaction  may  proceed  to  form  6-phosphogluconate 
(Figure  5) ^ the  substrate  for  phosphogluconate  dehydrongenase . 
6-Phosphogluconate  Dehydrogenase 

'Die  reaction  mixture  contained  50  miM  iRA-HCl  (pH  7.6), 

5 miM  CDJA,  0.5  mM  .N'.A.DP,  6.6  inM  MgSO^j,  1 mM  6-phosphogluconate,  end 
extract.  Tlie  product  was  ribulose-5-phosphate . 

Using  the  spectrophotometric  assays,  only  very  low  and  short- 
lived enzyme  activity  was  detected  by  these  procedures.  On  several 
occasions  the  reaction  reversed  after  starting.  Use  of  internal 
standards  and  commercially  prepared  enz>Tnes  showed  that  procedures 
were  valid.  Polyphenols,  resins,  terpenes  (Firenzuoli,  Vanni , and 
Mastronuzzi,  1969;  Anderson,  Lowe,  and  Vaughn,  1969),  quinones, 
and  tannins  formed  after  cells  are  ruptured  by  extraction  procedures 
(Anderson  and  Rowan,  1967)  and  other  endogenous  substances  in 
tissue  extracts  interfere  with  biochemical  reactions  a^id  inhibit 
enzyme  activity.  Attempts  to  prevent  oxidation  of  phenols  and 
quinones  with  reducing  agents  (Stokes,  Anderson,  and  Rowan,  1968; 
Wildes  et  al . , 1969),  to  remove  or  nullify  them  with  polyvinylpyrolli- 
done  (Jones,  Hulme,  and  Wooltorton,  1965;  Walker  and  Hulme,  1965; 
Loomis  and  Battaile,  1966),  and  to  extract  sufficient  proteins  for 
analysis  from  acetone  powders  failed,  as  did  efforts  to  concentrate 
enzyme  extracts . 

An  alternate  approach  proved  more  successful  and  was  used 
in  this  study.  Acetone  powders  were  made  from  green  tissue,  and 
the  enzymes  and  proteins  were  extracted  from  the  powders.  The 
quantity  extracted  was  too  small  for  spectrophotometric  use  but 
was  ample  for  electrophoretic  detection  and  colorimetric  measurements 


GLUCOSE -6 -PHOSPHATE  DEHYDROGENASE  AND  6-PHOSPHOGLUCONATE  DEHYDROGENASE 


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Figure  5.  Reactions  for  measuring  glucose-6-phosphate  dehydrogenase  and  6-phosphogluconate 
dehydrogenase 


37 


of  enzyme  activity.  Tne  technique  is  not  as  accurate  as  the  optical 
test,  but  it  has  been  used  successfully  (De.Jong,  Jansen,  and  Olson, 
1967;  Efron  and  Schwartz,  1968).  Considering  the  comparative  use 
made  of  these  data,  it  provided  an  acceptable  alternative. 

7 cet one  Powders --Preparati on  an.d  Protein  Ext r a c t i o n 

To  prevent  denaturation  of  enzymes  all  operations  were 
carried  out  at  temperatures  below  5 C with  cold  I'eagents,  tissue, 
and  glassware  (Hare,  1970). 

Twenty  grams  of  frozen  tissue  and  approximately  125  ml  of  80% 
acetone  were  "grated"  then  "liquified"  in  an  Oster  Blender.  Tlie 
brei  was  poured  through  a No.  60  soil  sieve.  Fibers  were  discarded 
and  the  suspension  sedimented  at  37,000  x g for  10  min.  T]ie 
supernatant  was  discarded  and  the  pellet  was  mixed  into  fresh  80% 
acetone.  The  suspension  was . sedimented,  as  before,  and  the  pellet 
blended  into  100%  acetone  using  a glass  homogenizer  and  teflon 
pestle.  After  vacuum  filtration  through  a plastic  filter-funnel, 
the  residue  was  washed  with  100%  acetone  until  white.  Tlie  residue, 
air-dried  by  vacuum  filti'ation,  was  sifted  through  No.  35  and  No.  100 
soil  sieves.  These  fines  were  stored  at  -20  C. 

Proteins  were  extracted  from  acetone  powders  with  a solution 
containing:  2.5  M urea,  22.5  niM  potassium  metabisulphite,  56.8 

mM  ascorbic  acid,  6.5  mM  dithiothreitol  (Clelands  reagent), 

"Tween  20",  tris  buffer  [tris  (hydroxymethyl)  amino  methane],  and 
water  to  give. a product  containing  0.004%  "Tween  20"  at  pH  8.5 
(Hare,  1970).  Protein  extracts  were  made  by  mixing  acetone  powder 
and  extracting  solution  200:3,  extraction  for  1 hr,  and  centrifugation 
at  37,000  X g for  10  min.  Tlie  supernatant,  extracted  with  a 
syringe,  contained  dissolved  proteins.  The  pellet  was  discarded. 


38 

Preparation  of  Polyacrylamide  Gels  and  Electrophore sis 

Preliminary  tests  were  made  comparing  polyacrylamide  gel 
formulations  and  layering  techniques  proposed  by  Bakay  and  Nyhan 
C1969),  Dar^is  (1964),  and  Hare  (1970).  Use  of  a large-pore 
sample  gel  as  an  anticonvection  medium  proved  inconvenient  and 
unnecessary;  the  high  concentration  of  urea  in  Hare's  extracting 
solution  served  as  well  when  layering  was  done  by  syringe  under 
the  upper  buffer  of  the  electrophoresis  chamber.  Separation  of 
glucose-6-phosphate  dehydrogenase  isoenzymes  was  enhanced  with  a 
large-pore,  spacer  gel,  but  the  clearest  definition  of  malate 
dehydrogenase  isoenzymes  was  obtained  without  one,  i.e.,  by  layering 
directly  on  the  small-pore,  running  gel.  Davis'  large-  and  small- 
pore  gels  gave  the  best  resolution  of  proteins. 

Buchler  Polyanalist  disc  electroplioresis  apparatus  was  used. 
Buffers  were  those  suggested  by  Hare:  tris-glycine  (pH  8.9) 

containing  bromphenol  blue  dye  in  the  upper  chamber  and  tris-HCl 
(pH  8.1)  in  the  lower  chamber.  Twelve  tubes  were  processed 
simultaneously  using  50  ma  of  current. 

Gels  were  precharged,  i.e.,  processed  without  a layer  of 
protein  extract,  to  remove  contaminants.  Protein  extract  was 
layered  on  gels  under  the  buffer  using  a syringe  calibrated  in 
pi.  The  urea  in  the  extract  prevented  dispersion  into  tlie  upper 
buffer.  Gels  developed  for  glucose-6-phosphate  dehydrogenase 
isoenzymes  and  for  protein  bands  were  layered  with  40  pi  of  protein 
extract  on  the  spacer  gel;  20  pi  of  extract  was  layered  directly 
onto  the  small  pore,  running  gel  used  for  development  of  malate 
dehydrogenase  isoenzymes  and  for  protein  bands.  Electrophoresis  was 
complete  when  the  colored  front  reached  the  lower  end  of  the  gel. 


39 


Detection  of  Protein  and  Isoenzyme  Bands 

Gels  vv'ere  removed  from  the  electrophoresis  tubes  with  a fine 
jet  of  water  then  placed  in  100  x 12  mm  test  tubes. 

Proteins  and  Dehydrogenase  Isoenzymes 

Gels  were  covered  with  lO-i  trichloroacetic  acid  then  agitated  in 
a reciprocal  shaker  for  30  min.  Three  drops  of  0.2%  coomassie  blue 
were  mixed  with  the  acid,  and  the  immersed  gels  were  stored  for  48  hr 
in  the  dark.  Stained  gels  were  rinsed  and  stored  in  8%  acetic  acid  in 
the  dark  at  4 C until  scanned  with  a Gilford  Model  2000  gel  scanner 
(densitometer) . 

Existing  techniques  for  preparing  substrates  to  color  isoenzymes 
of  a specific  enzyme  in  polyacrylamide  gels  were  used  (Johnson, 

Brannaman,  and  Zscheile,  1966;  Macko,  Honold,  and  Stalimann,  1967;  Roggen, 
1967). 

The  staining  procedure  involves  action  of  the  enzyme  on  its 
substrate  in  a coupled  reaction  that  results  in  the  reduction  of 
nitroblue  tetrazolium  (NBT)  to  a colored  product  (Goldberg,  1963). 

Bands  stain  blue.  The  intensity  of  the  stain  is  related  to  the  pH 
of  the  solution,  temperature,  length  of  incubation,  and  the  activity 
of  the  enzyme  (Gabriel  and  Wang,  1969) . 

Dietz  and  Lubrano  (1967)  recommended  90-min  incubation  for 
optimum  development  of  lactate  dehydrogenase  isoenzymes  and  cautioned 
against  using  less  than  45  or  more  than  120  min  for  quantitative  work. 

'Ihe  upper  limit  was  set  because  substrate  in  the  vicinity  of  the  most 
active  isoenzymes  is  exhausted  while  that  near  less  active  isoenzymes 
allows  staining  to  continue.  Ihis  was  true  with  malate  dehydrogenase 


40 


for  which  a 45-5iiin  incubation  period  \vas  used.  However,  comparisons  of 
staining  intensity  with  glucose-6-phosphate  dehydrogenase  subst7:ate 
showed  that  the  most  active  isoenzymes  continued  to  darken  even  after 
6 hr,  indicating  a low  level  of  enzyme  activity  and  an  adequate  supply 
of  sibstrate.  Background  staining,  attributed  to  protein  sislfliydryl 
groups  (Dietz  and  Lubrano,  1967),  occurred  witli  long  periods  of 
incubation,  so  development  of  isoenzymes  of  glucose-6-phosphate  de- 
hydrogenase was  reduced  to  3 hr  or  less. 

Hie  basic  incubation  media  was  prepared  using  two  solutions  to 
which  specific  substrate  and  pyridine  nucleotide  coenzyraes  were  added. 
Both  were  made  with  0.05  M tris-HCl  buffer  pH  7.5.  Solution  I contained 
30  mg  NBT  (dissolved  in  95%  ethanol)  and  100  mg  MgS04'7H20  dissolved 
in  50  ml  buffer.  Solution  II  was  composed  of  150  mg  EUTA  dissolved 
in  40  ml  hot  buffer  to  which. 3 rag  phenazine  methosulfate  (PMS)  was 
added  when  cool,  liie  solution  w^as  brought  to  50  ml  volume  with  buffer. 

Both  NBT  and  PMS  solutions  are  light-sensitive,  and  required  storage 
in  brown  bottles  and  use  in  subdued  light. 

'Phe  incubation  mixtures  for  developing  glucose-6-phosphate 
dehydrogenase  and  malate  dehydrogenase  bands  were  made  up  in  quantities 
to  develop  21  gels. 

Glucose-6-Phosphate  Dehydrogenase  and  Malate  Dehydrogenase 

Gels  were  inundated  in  an  incubation  mixture  containing  10  mg 
NADP,  84  mg  giucose-6-phosphate , 14  ml  solution  I,  and  14  ml  solution 
II,  then  incubated  at  37  C in  the  dark. 

I'lie  incubation  mixture  consisted  of  188  mg  malic  acid,  14  ml 
solution  I,  and  14  ml  solution  II  (adjusted  to  pH  7.5  with  NaOH) 
to  which  20  mg  NAD  was  added.  Gels  were  covered  with  the  incubation 


41 


mixture  and  incubated  at  37  C in  the  dark.  At  the  end  of  the 
incubation  period  S%  acetic  acid  was  substituted  for  the  incubation 
mixtures.  Gels  were  stored  at  4 C in  the  dark  until  scanned  on 
the  densitometer. 

Reaction  mixtures  for  staining  isoenzymes  that  involve  use  of 
one  or  more  accessory  enzymes  are  difficult  to  formulate.  Experi- 
ments aimed  at  developing  or  modifying  existing  procedures  (Bergmeyer, 
1965)  to  stain  fructose-1  6-diphosphate  aldolase,  glyceraldehyde-3- 
phosphate  dehydrogenase,  and  phosphoglycerate  kinase  isoenzyme  bands 
were  not  entirely  successful.  Bands  were  obtained  but  results 
were  not  consistently  reproducible. 

Individual  bands  were  identified  by  tlieir  position  relative 
to  the  dye  front  (Rf  value).  Activity  of  identified  isoenzymes 
measured  by  staining  intensity  was  quantified  using  heights  of 
densitometer  scanning  peaks.  Gabriel  and  Wang  (1969)  report  that 
quantification  of  isoenzyme  activity  using  reduced  tetrazolium 
is  accurate  for  comparative  purposes.  Comparisons  using  the 
number,  Rf,  and  activity  of  dehydrogenase  isoenzymes  were  made 
between  the  superior  tree  and  each  of  its  5 nonsuperior,  neighboring 
trees,  and  between  the  half-sibling  progeny  of  the  superior  tree 
and  that  of  each  of  its  neighbors  growing  on  two  soils.  .Similar 
comparisons  were  made  using  the  number,  Rf,  and  staining  intensity 
of  protein  bands. 

Sample  Size  and  Statistical  .^alysis 
Use  of  two  electrophoresis  chambers  permitted  processing  24 
gels  simultaneously  and  replication  of  samples  from  a single  location 


42 


and  soil  at  least  3 times.  Measurements  v;ere  obtained  from  scanned 
gels  representing  the  average  of  each  tree  x soil  x protein  combination. 

A randomized  complete  block  design  was  used  for  the  experiment 
involving  measurem.ents  of  isoenzjcnes  and  proteins.  Tlie  number  of 
oands,  Rf  values,  and  quantified  staining  intensity  data  froni  densitometer 
scannings  were  subjected  to  analysis  of  variance. 

Location  of  the  5 superior  trees  and  their  associated  nonsuperior 
contemporaries,  from  which  seeds  and  tissues  were  collected,  served 
as  blocks.  Comparisons  were  made  among  soils  on  vdiich  parent  trees 
grew  (original),  and  those  on  which  seedlings  were  grown  (Lakeland 
sand  and  Paola  sand),  and  among  trees  from  each  location.  Orthogonal 
partitioning  of  sums  of  squares  was  used  to  make  the  contrasts  specified 
under  soils  and  trees.  Dunnett's  procedure  (Steel  and  Torrie,  1960) 
was  used  to  compare  the  superior  tree  with  each  neighbor.  Selected 
comparisons  also  were  made  (at  a single  degree  of  freedom)  by  partitioning 
the  tree  x soil  interaction  sums  of  squares. 


RESULTS  AND  DISCUSSION 


Photoassimilation  of 

To  obviate  the  need  for  processing  all  seedling  parts,  time- 
course  studies  were  used  to  estimate  an  optim.uin  period  for  photo- 
assimilation of  ^'^C02.  Tlie  purpose  was  to  limit  time  for  translocation 
of  labelled  compounds  into  the  nonchlorophyllous  portions  of  the  seedling, 
yet  permit  incorporation  of  easily  measurable  quantities  in  green 
tissue.  Radioactivity  of  the  ethcinol-soluble  fraction  of  needles  and 
green  stem,  stem,  and  roots  was  measured  for  seedlings  allowed  to 
photoassimilate  ^'^C02  for  15,  30,  60  and  120  min. 

Results  summarized  in  Figure  6 show  that,  with  minor 
exceptions,  there  was  a orogressive  increase  in  radioactivity  in 
stem  and  root  tissue  with  the  length  of  the  photoassimilation 
period,  and  the  proportion  of  activity  in  green  tissue  decreased  as 
the  length  of  photoassimilation  increased.  It  appears  that  even 
with  photoassimilation  as  short  as  15  min,  ample  time  is  provided 
for  some  translocation  of  labelled  compounds  to  the  roots.  The 
proportionately  high  concent  cation  of  radioactivity  in  the  stem, 
compared  to  root  tissue  for  all  lengths  of  exposui’e  suggests  that 
the  stem  of  young  sand  pine  seedlings  serves  more  as  storage 
tissue  than  primarily  as  an  avenue  for  translocation.  Tliis  does  not 
discount  possibilities  that  some  C02-fixation  may  occur  in  jion-green 
tissue  or  that  a high  rate  of  metabolism  in  the  roots  may  catabolize 
and  respire  some  labelled  compounds.  Extrapolation  of  the  data  suggested 
a 10  min  photoassimilation  period  as  near  optimum. 


43 


LEVEL  OF  ACTIVITY  IN  CLOSED  SYSTEM  = 44,382,000  CPM 


44 


CM 


Pi 


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PJ 

H 

3 

2 


o 

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Figure  6.  Distribution  of  radioactivity  in  seedlings  allowed  to  photoassimilate  ^“^CO, 


45 


Results  of  the  tiir.e-course  experiment  raised  two  questions: 

1)  would  assimilation  of  ^^C02  and  CO2  continue  during  the  post-illumination 
period  while  the  chamber  was  being  cleansed  of  radioactive  gas  and 
seedlings  were  being  processed  for  freezing?  2)  'V.liy  was  such  a small 
proportion  of  the  44  million  cpm  released  into  the  closed  system  utilized 
even  after  a 2 hr  photoassimilation  period?  Experiments  were  conducted 
to  answer  these  questions. 

Tlie  first  was  designed  to  answer  question  1 and  to  test  the 
conclusion  that  a 10  min  photoassimilation  period  was  near  optimum 
for  fixing  measureable  amounts  of  labelled  carbon  in  green  tissue 
without  allowing  appreciable  amounts  to  translocate  to  the  stem  and 
roots,  i.e.,  to  limit  radioactivity  primarily  to  green  tissue. 

Working  at  night  to  reduce  the  likelihood  of  contamination  by 
incident  daylight,  com.parison  was  made  of  the  radioactivity  in 
ethanol  extracts  of  green  tissue,  stem,  and  roots  between  seedlings 
subjected  to  a)  preconditioning  and  exposure  to  ^‘^C02  for  10  min 
in  darkness  or  b)  preconditioning  and  pliotoassimilation  for  10 
min  using  2,000  ft-c  light.  Post-induction  periods  in  both  treatments 
were  in  darkness,  and  seedlings  were  processed  for  preliminary 
freezing  in  subdued  light  (just  enough  to  ascertain  that  all  sand 
was  washed  from  roots) . 

Results  presented  in  Figure  7 support  the  previous  contention 
that  pliotoassimilation  for  less  than  15  min  confines  metabolites 
with  14c  to  g.reen  tissue  without  permitting  appreciable  amounts  to 
translocate  to  the  stem  and  roots.  Reducing  the  photoassimilation 
period  from  15  to  10  min  increased  the  proportion  of  radioactivity 
in  green  tissue  by  about  3%  compared  to  activity  in  stem  and 
roots.  It  also  reduced  radioactivity  by  70%  in 


46 


light  dark 

Figure  7.  Distribution  of  radioactivity  in  seedling  tissues  exposed  to 
^C02  in  the  light  and  dark 


47 


green  tissue,  75%  in  stems,  and  87%  in  roots.  Shorter  photoassimilation 
periods  might  have  increased  the  proportion  of  radioactivity  in  green 
tissue  and  greatly  limited  translocation  to  the  stem  and  roots,  but 
extrapolation  of  15  and  10  min  data  suggests  that  radioactivity  in 
green  tissue  also  might  be  lowered  to  a level  of  questionable  utility. 
For  purposes  of  this  study  a 10  min  photoassimilation  period  appeared 
near  optimum. 

In  the  dark  radioactivity  was  recorded  in  the  stem,  but  none  in 
the  roots  or  green  tissue  of  all  4 seedling  replicates.  Results, 
while  not  analyzed  statistically,  emphasize  the  need  to  extinguish 
light  at  the  conclusion  of  the  photoassimilation  period  and  to  process 
seedlings  in  subdued  light. 

The  large  discrepancy  between  the  radioactivity  of  labelled 
carbon  in  the  system  and  the  amount  photoassimilated  has  at  least 
5 possible  explanations: 

1.  Uptake  of  CO2  was  limited  by  some  unexplained  physiological 
condition (s) . 

2.  Preferential  uptake  of  CO2  over  ^“^002 . 

3.  An  excess  of  C02was  used. 

4.  Activity  was  lost  during  preparation  of  ethanol  extracts  or 
was  masked  by  chlorophyll  and  other  extraneous  material. 

5.  Not  all  the  radioactive  carbon  was  released  from  KHI4CO3 
by  the  lactic  acid. 

The  system  was  gas  tight.  Photo-  and  dark-respiration  do  not  account 
for  the  large  discrepancy.  Possibilities  1 and  2 are  beyond  the 
scope  of  this  investigation,  and  3 was  intentional.  Experiments  were 
undertaken  to  test  4 and  5. 


48 


Aliquots  of  green  tissue  extract  prepared  from  5 sand  pine 
seedlings  were  pipetted  into  scintillation  vials  to  form  an  arith- 
metic series  from  0.5  through  5.0  ml  in  0.5  ml  increments.  A 
blank  of  95%  ethanol  was  used.  To  each  vial  10  ]jl  ^^C-sucroso  was 
added.  All  w’ere  evaporated  to  dryness,  tlien  tlie  residue  was  taken 
up  in  0.5  ml  absolute  alcohol  and  diluted  with  10  ml  BBOT  scintillation 
cocktail.  One  additional  vial  containing  2.5  ml  green  tissue  extract 
was  similarly  prepared  and  processed  except  that  the  extract, 
including  ^^C-sucrose,  was  clarified  with  charcoal  before  evaporating 
the  liquid.  Counting  efficiency  and  cpm  were  recorded  on  identical 
liquid  scintillators  at  two  cooperating  laboratories  (Agronomy  and 
Pesticides). 

Chlorophyll  in  the  scintillation  fluid  lowered  both  counting  efficiency 
and  cpm.  High  concentrations  of  chlorophyll,  such  as  those  found  in 
tissue  from  high  nitrogen  fertilizer  treatments,  were  most  seriously 
affected.  Effectiveness  of  the  scintillators  was  lowered  in  direct 
proportion  to  the  amount  of  chlorophyll  present.  Clarification  with 
charcoal  improved  counting  efficiency  by  800%  and  increased  cpm  by 
250%  in  the  vial  containing  2.5  ml  of  chlorophyll-containing  extract. 

Some  loss  of  radioactivity  occurred  during  clarification  but,  considering 
gains  experienced,  it  was  considered  tolerable.  At  best,  however, 
the  counting  efficiency  was  only  0.70  in  scintillation  fluid  containing 
no  green  tissue  extract,  indicating  that  the  cocktail  or  absolute 
ethanol  lowered  counting  efficiency.  Ihese  possibilities  were  tested. 

Results  of  the  tests  showed  that  the  cocktail  and  the  absolute 
ethanol  used  with  scintillation  equipment  in  the  Forest  Physiology 
and  Genetics  Laboratory  (F.P.G.L.)  caused  quenching  in  scintillator 


49 


counters  at  cooperating  laboratories.  The  cooperators  equipment  had 
been  standardized  against  cocktail  other  than  BBOT.  To  compensate 
for  quenching  caused  by  chlorophyll  and  ethanol  and  for  differences 
in  cocktail,  curves  were  drawn  to  equate  all  measurements  of  radioactivity 
at  100%  counting  efficiency  regardless  of  cooperator  equipment  used. 

Figure  8.  BBOT  alone  was  responsible  for  a reduction  in  counting 

of  more  than  20-s.  Absolute  ethanol  caused  a further  reduc- 
tion of  about  11%.  Increasing  the  proportion  of  BBOT  to  absolute 
ethanol  improved  efficiency  by  about  2%  but  reduced  cpm  by  more  than 
14%.  Linear  regressions  of  the  form  Logg  AES  Ratio  = a+b  Logg 
cpm  were  fitted  to  a plot  of  the  data.  Test  of  the  regression  by 
analysis  of  variance  showed  that  the  probability  of  obtaining  an 
F value  larger  than  that  obtained  for  regression  was  less  than  0.0001 
for  cooperator  equipment.  No  meaningful  loss  of  accuracy  occurred 
from  fitting  straight  line  functions  to  the  data.  The  slope  of  each 
curve  appears  to  be  unique  for  each  scintillator. 

Seedlings  appear  to  utilize  only  a minute  amount  of  the  ^‘^C02 
released  into  the  photoassimilation  chamber.  Possibly  not  all  of  the 
20  yc  of  activity  (45  million  dpm)  was  evolved  from  Kh1^C03  by 
lactic  acid  even  though  two  equivalents  of  acid  were  used  to  one  of 
the  bicarbonate. 

To  test  the  effectiveness  of  the  acid,  a comparison  was  made  of 
radioactive  carbon  photoassimilated  by  seedlings  when  10  ml  of 
concentrated  lactic,  hydrochloric,  or  sulfuric  acid  were  used. 
Stoichiometrically,  this  provides  twice  the  amount  of  lactic  and 
hydrochloric  and  4 times  the  ajnount  of  sulfuric  acid  needed  to 
evolve  500  ppm  of  CO2  containing  20  yc  of  activity  from  the  potassium 


EFFICIENCY 


50 


Figure  8.  Quenching  curves  developed  to  compensate  for  loss  of 
counting  efficiency 


I 


51 


bicarbonate.  To  verify  results  of  a previous  experiment,  which 
indicated  that  postil luinination  processing  of  seedlings  should  be 
done  in  darkness,  one  additional  treatment  was  included.  Two 
equivalents  of  lactic  acid  w’ere  used  to  evolve  > but  liglits  v/ere 
left  on  for  an  additional  5 m-’  n following  the  10  min  photoa  ;siii  ilation 
period  (while  CO2  in  the  chamber  was  trapped).  'Ilien,  seedlings 
were  processed  in  fluorescent  rather  than  subdued  light.  Adjustments 
were  made  for  quenching,  and  cpm  were  expressed  per  gram  of  fresh 
tissue  weight. 

Inorganic  acids  more  effectively  evolved  CO^  from  KHCO3  than 
lactic  acid.  Figure  9.  On  an  equivalent  basis  HCl  was  as  effective 
as  H2S0^,  but  in  this  experiment,  only  two  equivalents  of  HCl  were 
used  as  compared  to  four  of  H2S0^. 

Photoassimilation  of  continued  during  5 additional  min 
of  light  while  the  chamber  was  cleansed  of  ^"*002  . Tlie  exact  amount 
could  not  be  determined  because  seedlings  subjected  to  the  additional 
photoassimilation  period  also  were  processed  in  fluorescent  rather 
than  subdued  light.  Some  loss  of  have  occurred  to  the  atmos- 

phere due  to  photorespiration. 

Clarification  o f Ex tracts  and  Quen ching 

Extraneous  material  in  ethanol  extracts  caused  quenching,  i.e., 
loss  of  counting  efficiency  and  a reduction  in  recorded  cpm,  in  the 
liquid  scintillator.  Dark  green  extracts  from  seedlings  supplied 
high  rates  of  N proved  particularly  troublesome.  Attempts  to 
rcm.cve  the  chlorophyll  by  filtration  or  centrifugation  failed. 

Powdered,  activated  charcoal  was  lased  routinely  in  previous 
experiments  as  a clarifying  agent;  and  even  though  some  loss  of 


52 


CO 

a 


50 


4 Equiv. 


CO 

o 

X 

H 


40 


H 

X 

CJ 

J—J 

w 


30 


X 

CO 

w 

cc 

PU 


2 Equiv. 


CJ 

Pi 

w 

a. 

S 

a 

u 


20 


2 Equiv. 


10 


2 Equiv. 


LACTIC  HCL  H2SO4 


LACTIC 


PROCESSED : IN  DARKNESS 


IN  LIGHT 


Figure  9.  The  C incorporated  into  green  tissue  of  Pinus  Clausa  in 
response  to  different  founts  and  kinds  of  acid  used  to 
release  ^‘^C02  from  Kh14c03 


53 


radioactivity  occurred,  gains  in  counting  efficiency  moi'e  than 
compensated  for  losses.  Powdered,  activated  alumina  was  compared 
with  powdered,  activated  cliarcoal  to  provide  a more  efficient 
clarifying  agent. 

Ethanol  extracts  from  2 s 2ts  of  seedlings  (each  represented  by 
the  4 fertilizer  treatments)  were  prepared  from  seedlings  that  had 
photoassimilated  Color  of  the  extracts,  ranged  from  light  to 

dark  green  (no  color  charts  for  foliage  were  available). 

NjPj  NjP^  NjPj 

Dark  green Light  green 

One  set  of  extracts  was  clarified  with  activated  alumina 
(80-200  mesh  size  chromatogranhic  grade)  using  3 additions  of 
approximately  0.5  g each  plus  3 min  spinning  at  maximum  speed  on  a 
clinical  centrifuge  after  each  addition.  Com.parison  with  untreated 
extiact  showed  no  color  change  although  tlie  alumina  had  attained 


a light  yellowish-green  color. 

Tne  other  set  of  extracts  was  clarified  with  powdered  activated 
charcoal  using  3 additions  of  approximately  0.3  g each,  as  above.  All 
clarified  extracts  were  light  yel low'ish-green  and  only  a slight 
difference  in  color  remained  between  extracts  of  N2P^  and  NjP^  fertilized 
seedlings.  Because  alumina  failed  to  clarify  the  extracts,  they 
were  treated  with  charcoal.  Meaningful  differences  in  counting 
efficiency  or  cpm  between  charcoal  clarified  and  alumina  plus  charcoal 
clarified  extracts  were  attributed  to  alumina. 

Figure  10  shows  that  when  both  counting  efficiency  and  retention 
of  radioactivity  are  considered,  clarification  with  charcoal  was  as 
good  or  superior  to  clarification  with  both  alumina  and  charcoal. 

Alumina  by  itself  was  not  an  efficient  clarifying  agent. 


CPM  PER  GRAM  FRESH  WEIGHT  IN  THOUSANDS  COUNTING  EFFICIENCY 


54 


230 

210 

190 

170 

150 

130 

110 

90 

70 

50 

30 


Figure  10.  Comparison  of  clarifying  agents 


55 


Objectives  of  another  series  of  experinents  were:  to  identify 

metabolic  pathways  most  responsible  for  fixation  of  atmospheric 
carbon  in  green  sand  pine  seedling  tissue;  to  determine  the  affect 
of  each  of  the  4 levels  of  fertilizer  on  the  seedlings,  on  radio- 
activity in  the  ethanol-soluble  fraction  of  green  tissue,  and  on 
the  relative  amounts  of  labelled  sugars,  organic  acids,  and  amino 
acids  produced. 

Ethanol  extracts  made  from  green  tissue  of  fertilized,  3- 
month-old  sand  pine  seedlings,  after  HCO2  was  photoassimilated  for 
10  min  at  2,000  ft-c  and  25  1 C,  were  fractionated  on  ion  exchange 

columns.  Radioactive  counts  were  made  of  sugar,  organic  acid,  and 
amino  acid  fractions.  Sugars  and  acids  were  separatee,  i ico 
constituent  compounds  chromatographical ly,  for  identification,  and 
radioautograms  were  made  of  TLC  plates  to  permit  comparison  of 
radioactivity  among  constituents. 

Table  4 shows  the  actual  and  proportional  distribution  of 
in  the  ethanol  soluble  fractions,  llie  insoluble  fraction,  composed 
primarily  of  cellulose,  hemicellulose,  and  lignin, was  not  assayed. 
Shiroya  et  al.  (1962,  1966j  working  with  white  and  red  pine  seedlings 
and  Balatinecz,  Forward,  and  Bidwell  (1966)  working  with  8-month- 
old  jack  pine  found  no  more  than  10%  of  photoassimilated 
in  the  ethanol  insoluble  fraction.  Extrapolation  of  their  data 
suggests  that  virtually  all  the  photoassimilated  in  10  min 
was  contained  in  ethanol-soluble  compounds.  In 'O-raonth-old  sand 
pines  Riech  (1970)  reported  very  little  translocation  of  labelled, 
ethanol-soluble  compound  from  needles  supplied  by  photoassimilated 
^^C02,  even  after  8 hours. 


56 


Table  4 . --Distribution  of  photoassimilated  14C  in  green  sand  pine 
seedling  tissue 


Ethanol  Soluble  Fractions 


Organic  Acid  Amino  Acid  Total 

lo^/g  fresh  tissue 

55.7  13.8  4.8  74.3 

. Percent  of  fraction 

75.0  18.6  6.4  100.0 


57 


Of  the  ethanol-soluble  fraction,  sugars  contained  75%,  organic  acid 
19-6,  and  amino  acids  6%  of  the  labelled  carbon  in  green  tissue. 

About  40-6  of  the  activity  was  lost  during  fractionation  of  the 
ethanol  extract  on  ion  exchange  columns.  Although  this  loss  is 
approximately  2 1/2  times  as  great  as  that  reported  by  Riech  using 
the  identical  procedure,  the  proportionate  distribution  of  he 
reported  in  6-month-old  sand  pines  wa.s  almost  identical  i.e., 

76%  sugars,  17%  organic  acids,  and  7%  amino  acids. 

Sugars 

Glucose,  fructose,  and  galactose  were  the  3 most  common  sugars  identified 
for  seedlings  raised  at  all  levels  of  fertilization.  Rf  values 
for  glucose  and  frucLOse  overlapped  (fable  3)  but  were  differentiated 
by  color.  UTien  sprayed  with  developer  and  heated,  glucose  stained 
brown,  and  fructose  yellow.  Rf  values  for  glucose  and  fructose 
differed  enough  from  galactose  to  avoid  confusion,  but  Rf's  for 
galactose  and  sucrose  were  similar.  Here,  too,  color  was  used  to 
differentiate  oetween  them;  galactose  was  brown,  and  sucrose  was 
brownish-yellow.  One  other  band  developed  primarily  in  the  extract 
from  seedlings  raised  at  low  levels  of  nitrogen.  Its  Rf  identified 
it  as  a pentose,  but  it  bracketed  the  ranges  of  ribose,  arabinose, 
and  mannose.  The  brownish-blue  color  indicated  it  was  arabinose. 

Tlie  chromatogram  illustrated  in  Figure  11  shows  other  bands  at 
relatively  high  Rf  values,  but  they  were  either  faint  or  not  present 
at  all  levels  of  fertilization.  They  were  not  specifically  identified; 
yet,  since  Rf  values  in  sugars  are  inversely  proportional  to  molecular 
weight  and  number  of  hydroxyl  groups  (Lewis  and  Smith,  1969)  or 
the  number  of  carbons,  this  suggests  they  were  probably  tetroses  or 


58 


1 


59 


Figure  12.  Radioautogram  of  a sugar  TLC  plate  (6  weeks  exposure) 


60 


Figure  13.  Radioautogram  of  the  same  TLC  plate  used  in  Figure  12  (2  weeks  exposure) 


61 


trioses.  llie  bands  were  for  the  most  part  in  extracts  from  seedlings 
raised  at  high  levels  of  N and  P. 

Radioautograms  of  TLC  plates  show  that  most  of  the  14^  ‘ 

contained  in  glucose  and  fructose,  less  in  galactose,  virtually 
none  in  high  Rf,  low  molecular  weight  sugars,  and  none  in  pentoses 
(Figures  12  and  13).  No  difference  in  radioactivity  between  glucose 
and  fructose  was  apparent  here  even  though  the  green  tissue 
included  active  apical,  leaf,  and  stem  meristem. 

Rangnekar  and  Forward  (1969)  reported  differential  fixation  of 
^4c  in  fructose  and  glucose  following  6 days  of  14^2  assimilation. 
From  2.7  to  8.4  times  as  much  radioactivity  was  found  in  fructose 
as  in  glucose  in  the  stem,  root,  and  bud  of  red  pine  seedlings. 

The  pattern  was  reversed  in  needles:  1.4  times  as  much  14^ 

recorded  in  glucose.  Tlie  high  proportions  in  active  meristematic 
tissue  was  attributed  to  metabolism  of  the  glucose  moiety  of 
translocated  sucrose  and  the  presumed  sequestration  of  fructose 
within  a cell  compartment  or  in  the  individual  cell.  This  explanation 
is  in  agreement  with  the  theory  for  higher  plants.  Sucrose  acts  as 
a protective  derivative  and  source  of  glucose,  the  primary  metabolite 
of  all  living  organisms  (Arnold,  1968). 

Some  labelled  carbon  remained  at  and  near  the  origin.  The 
concentration  was  particularly  high  for  seedlings  raised  at  the 
high  N level.  Their  low  mobility  with  respect  to  sucrose 
and  raffinose  suggested  that  they  were  oligosaccharides,  possibly 
verbascose,  composed  of  sucrose  plus  3 galactose  units.  Presence 
of  oligosaccharides  containing  sucrose  might  serve  to  explain 
absence  of  sucrose  on  the  chromatograms.  A body  of  evidence  exists 


62 


to  show  that  sucrose  is  a primary  translocate  in  higher  plants 
(Clauss,  Mortimer,  and  Gorham,  1964;  Gordon  and  Larson,  1968; 

Shiroya  et  al . , 1962;  IVillenbrink,  1966;  Hofstra  and  Nelson,  1969), 
including  conifers.  Hida,  Sacko,  and  ILnrada  (1962),  however, 
found  that  the  sucrose  content  in  pine  needles  appeared  lower  than 
in  foliage  of  other  conifers.  In  some  plants  raffinose,  (Pridham, 
Walter,  and  Worth,  1969)  stachyose,  and  verbascose  (Webb  and  Burley, 
1964,  Trip,  Nelson,  and  Krotkov,  1968)  were  found  among  translocates 
(sucrose  plus  1,  2,  and  3 galactose  units,  respectively).  It 
seems  apparent  that  oligosaccharides  wore  present.  Tliey  may  serve 
as  translocates  in  young  sand  pine  seedlings. 

Tlie  extract  from  one  seedling  fertilized  at  the  high  level  of 
N and  low  level  of  P remained  at  the  origin  of  the  TLC  plate. 

Extract  from  all  other  seedlings  raised  under  this  fertilizer 
regime  migrated  upward  during  separation.  iTie  seedling  is  believed 
to  have  been  moribund.  Seedlings  raised  at  low  P levels  (P]^) 
suffered  comparatively  high  mortality  in  both  pots  and  tubules. 
Mortality  am.ong  the  faster  growing  N2PJ  seedlings  was  higher  than 
among  slower  growing  N^Pj^  seedlings.  Dead  and  dying  seedlings  were 
characterized  by  a constriction  of  the  stem  at  groundline  reminiscent 
of  damping  off  disease  (Figure  14) . 'Hie  constriction  and  area 
immediately  adjacent  to  it  was  black.  It  appeared  charred.  Dr. 

R.  Schmidt,  Forest  Pathologist  at  F.P.G.L.,  identified  a species 
of  Verticillium  in  one  of  several  tissue  sample  cultures.  Alexopoulos 
(1952)  recognizes  Va'x^'t’VQ'Ll^'L'tw^  as  a cause  of  wilt  disease  in  many 
plants  and  as  a fungus  associated  with  damping-off. 


63 


Figure  14.  Moribund  seedling  showing  constriction  near  groundline 


64 


Another  possible  cause  of  mortality  among  seedlings  raised 
at  the  low  level  of  P might  have  been  chemical  burn.  HCl  was  used 
to  adjust  the  acidity  of  nutrient  solutions  to  pH  5.85  + 0.05. 

Prior  to  adjustment  solutions  containing  the  low  level  of  P were 
pH  9.8  and  pH  10.5,  whereas  those  containing  the  high  level  were 
pH  3.5  and  pH  5.8.  Accumulation  of  Cl“  during  the  2 weeks  between 
flushings  of  plant  containers  with  deionized  water  could  have 
resulted  in  a Cl  build-up  and  bui'n. 

Regardless  of  the  cause  of  death,  seedlings  supplied  the  NCP 

^ 1 

nutrient  solution  had  a comparatively  high  rate  of  mortality.  The 
possibility  exists  that  one  healthy-looking  but  moribund  seedling 
was  used  in  these  experiments.  If  this  were  a fact,  assimilation 
processes  may  have  all  but  ceased  thereby  causing  a low  level  of 
C fixation  in  sugars.  More  likely,  however,  is  the  possibility 
that  the  stem  was  girdled  causing  accumulation  of  translocation 
products  in  the  stem  and  green  tissue  above  the  girdle.  If  these 
products  were  high  molecular  weight  oligosaccharides,  such  as 
stachyose  or  verbascose,  their  movement  from  the  origin  would  be 
slight.  Idle  seedlings'  moribund  condition  would  permit  progressively 
less  assimilation  of  in  comparatively  low  caibon  sugars  such  as 
fructose,  glucose,  and  galactose  and  reduced  respiratory  loss  of 
labelled  compounds.  Subsequent  coupling  with  previously  formed 
sucrose  might  result  in  an  accumulation  of  translocated  ^Re- 
labelled high  carbon  sugars,  such  as  stachyose  and  verbascose,  at 
the  origin  of  the  TLC  plate.  Examination  of  the  radioautogram 
shows  this  to  have  been  the  case. 


Organic  Acids 


65 


Incorporation  of  14c  in  the  organic  acid  fraction  amounted 
to  only  about  one-fourth  that  in  sugars,  (Table  4).  Separation 
by  TLC  required  several  treatments  with  solvent  to  obtain 
separation  for  identification  of  some  components.  Figure  15. 
Exposure  of  plates  to  x-ray  film  for  two  weeks  yielded  no  clearly 
discernible  bands  of  radioactivity;  6 weeks  exposure  was  required 
to  obtain  faint  bands.  The  intensity  of  the  bands  attests  to 
the  low  activity  obtained  on  liquid  scintillation  equipment. 

Several  bands  appeared  on  the  radioautograms  that  did  not 
correspond  to  those  obtained  visually  on  TLC  plates.  These  were 
labelled  "hot"  on  the  chromatogram.  "Hot"  bands  were  found  only 
in  syrupy  extract.  The  Rf  of  one  "hot"  band  coincided  with  that 
of  malic  acid  standards,  another  with  glutamic  acid.  Glutamic 
acid  is  a dicarboxylic  amino  acid  formed  from  the  organic  acid 
c^-ketoglutarate  and  NH^ . An  intermediate  is  “^-iminoglutarate  which 
requires  NADH  + H+  and  glutamic  dehydrogenase  to  catalyze  the 
second  reaction  (Devlin,  1968) . It  is  conceivable  that  oc_ 
iminoglutarate  or  the  acidic  glutamic  acid  was  absorbed  on  the 
50w  X 8,  H+-form  resin  to  become  a contaminant  contributing  to 
the  syrupy  consistency  of  the  extract. 

Malic  acid  was  the  only  organic  acid  identified  containing 
detectable  amounts  of  ^4q_ 

Amino  Acids 

This  fraction  of  ethanol-soluble,  green  tissue  extract 
contained  the  least  radioactivity,  about  one-twelfth  of  that  in 
sugars.  Activity  was  so  low  that  spots  could  barely  be  detected 


66 


Hatched  bands  are  unknowns 

Organic  acid  standards  are  labelled:  glutamic  acid  (G) , 

oxalic  acid  (0) , ascorbic  acid  (A) , and  malic  acid  (M) 

Radioactive  bands  (HOT)  appeared  in  syrupy  (S)  extract 


67 


on  x-ray  film  after  6 weeks  of  exposure.  Prints  could  not 
be  made. 

Only  extract  from  trees  fed  the  higji  level  of  nitrogen 
contained  radioactive  spots.  Figures  16  and  17.'  They  v/ere 
identified  by  using  Soltanabedi' s (1966)  amino  acid  map  as; 
glutamic  acid,  aspartic  acid,  and,  because  of  the  close  proximity 
of  spots,  either  lysine  or  arginine,  most  probably  the  latter. 

Labelled  malic  acid,  glutamic  acid,  and  aspartic  acid  suggest 
activity  of  the  tricarboxylic  acid  cycle,  amination  of 
ketoglutarate  to  glutamic  acid,  and  possibly  transamination  to  form 
aspartate  leading  to  arginine  in  the  urea  cycle  (IVilson,  King, 
and  Burris,  1954).  Because  of  the  extremely  low  incorporation 
Or  C in  amino  acids,  no  further  work  was  done  with  amino  acids 
and  the  enzymes  involved  in  their  synthesis. 

Effect  of  Nutrient  Level  on  Seedling 
Morphology  and  Incorporation 

Distribution  of  weight  and  in  seedlings  supplied  7.5 

ppm  (%)  or  75.0  ppm  (N2)  N,  and  15.0  ppm  (Pi)  or  150.0  ppm 

Pj  is  summarized  in  Table  5.  The  proportional  distribution 
of  weight  and  radioactivity  as  influenced  by  N and  P nutritional 
levels  is  shown  in  Table  6. 

Color  and  Weight 

Foliage  was  darker  green  in  N2  than  Nj  treatments  and 
darkest  in  the  N2P1  treatment.  P,  by  itself,  liad  no  noticeable 
Influence  on  color.  (See  re-^ults  of  experiment  testing  clarifying 
agents  on  page  53.) 

N more  than  P influenced  seedling  weight  and  size.  The  entire 
seedling  and  each  of  its  component  parts  was  larger  and  heavier  • 


YELLOW 


glutamic  acid 


aspartic 

acid 


arginine 

or 

lysine 


ORIGIN 


Figure  16,  Amino  acid  TLC  plate  for  fertilizer  treatment  N2PJ 


* 


Radioactive  spots  are  labelled 


69 


0 

glutamic  acid 


6 


aspartic 

acid 


^^^^arginine 
or 

lysine 


1. 


ORIGIN 


2. 


Figure  17.  Amino  acid  TLC  plate  for  fertilizer  treatment  N2P2 


Radioactive  spots  are  labelled  * 

One  * spot  (dotted  outline)  did  not  appear  on  the  TLC  plate 


70 


in  N2  than  Nj  treatments.  The  effect  of  P was  not  as  pronounced 
and  appeared  to  have  been  centered  in  green  tissue  and  roots. 

P2  treatments  contained  the  heaviest  seedlings.  The  N.,Po 
fertilizer  regime  produced  the  largest  and  heaviest  seedlings. 

Ratios  between  green  and  nongreen  tissue  weight  were 
virtually  unaffected  by  P but  strongly  influenced  by  N.  The 
ratio  was  lowest  for  seedlings  which  suggests  that,  like  the 
more  common  top-root  ratio,  a favorable  balance  existed  between 
green  and  nongreen  tissue.  This  was  expected  because  N2  treat- 
ments produced  seedlings  with  the  most  green  tissue. 

Fertilizer  combinations  most  conducive  to  green  tissue 
production  contained  the  high  level  of  N.  N2^  produced  seedlings 
with  heavy  foliage,  stem,  and  roots.  N2P2  produced  proportionately 
less  root  and  stem  tissue  and,  therefore,  seedlings  with  the 
highest  green-nongreen  tissue  ratio.  Seedlings  grown  in  N^Pj 
were  smallest  but  the  weight  distribution  between  green  and  nongreen 
tissue  was  most  equally  balanced. 

Incorporation 

Foliage  of  N2-fed  seedlings  was  heavier  and  darker  green 
than  those  fed  Nj . It  contained  more  chlorophyll  and  photo- 
assimilated  more  ^^C02,  consequently,  green  tissue  extracts  from 
N2 -supplied  seedlings  were  more  radioactive.  The  affect  of  N 
and  P on  C incorporation  becomes  apparent  only  when  radioactivity 
is  adjusted  for  differences  in  tissue  weight,  i.e.,  when  expressed 
on  a weight  of  green  tissue  basis. 

Both  P and  N influenced  the  level  of  radioactivity  in 
ethanol  extract  and  most  of  its  component  fractions.  Highest 


71 


Table  5. --Seedling  weight  and  photoassimilated  distribution 
in  response  to  nutrients 


NUTRIENT 

REGIME 

ITEM 

NjPl 

N1P2 

N2P1 

N2P2 

Weight  in  grams 

Entire  seedling 

0.375 

0.425 

0.929 

1.196 

Needle  + green  stem 

.146 

.168 

.542 

0.675 

Stem 

.024 

.024 

.042 

.048 

Roots 

.205 

.233 

.345 

.473 

Ratio 

Green/nongreen  wt. 

Adj . cpm/g  green  tissue 

.594 

X 10^ 

.675 

1.367 

1.264 

Ethanol  extract 

55.2 

69.0 

41.1 

74.7 

Sugars 

38.9 

58.0 

54.9 

71.2 

Organic  acids 

10.9 

22.0 

10.0 

12.5 

Amino  acids 

5.5 

3.0  - 

5.9 

4.6 

Nutrient  treatments  were:  7.5  ppm  (Nj)  or  75.0  ppm  (N^,)  of 

N and  15.0  ppm  (Pj)  or  150.0  ppm  (P2)  of  P 


72 


Table  6. -Influence  of  N and  P fertilizer  on  the  distribution  of 
weight  and  radioactivity 


NUTRIENT  PJEGIME 


NITROGEN 

LEVELS 

PHOSPHORUS 

LEVELS 

N2 

Pi 

P2 

ITEM  (7 

.5  ppm) 

(75  ppm) 

(15  ppm) 

(150  ppm) 

of  seedlings- 

Heaviest  seedling 

5.6 

94.4 

44.4 

55.6 

Heaviest  green  tissue 

0.0 

100.0 

50.0 

50.0 

Heaviest  stem 

11.1 

88.9 

50.0 

50.0 

Heaviest  root 

5 .6 

94.4 

44.4 

55.6 

Lowest  green-nongreen 
tissue  wt.  ratio 

100.0 

0.0 

50.0 

50.0 

Highest  adj . cpm  per 
gram  green  tissue 

Ethanol  extract 

55 . 6 

44.4 

44.4 

55.6 

Sugars 

37.5 

62.5 

12.5 

87.5 

Organic  acids 

50.0 

50.0 

50.0 

50.0 

Amino  acids 

12.5 

87.5 

62.5 

37.5 

i 


73 


C incorporation  in  the  extract  was  recorded  in  P2  and 
treatments.  Treatment  combinations  with  the  highest  radioactivity 
were  N2r*2  and  Njp2' 

Sugars  contained  75%  of  the  photoassimilate  -*-4c  and,  in 
this  fraction,  tlie  level  of  activity  was  influenced  almost 
exclusively  by  P.  Seedlings  supplied  NU  were  more  radioactive  than 
those  supplied  Nj , but,  on  the  average,  P contributed  more  to 
incorporation  than  N.  Seedlings  grown  in  N2P^  contained  the 

most 

Interpretation  of  the  affects  of  N and  P on  fixation  of 
in  organic  and  amino  acids  is  confounded  by  presence  of,  what 
appears  to  be,  glutamic  acid  in  both  acid  fractions.  To  facili- 
tate interpretation,  the  presumed  contaminant  in  the  organic  acid 
fraction  was  considered  to  be  “-iminoglutarate,  the  oxidized  • 
precuisor  of  glutamic  acid,  lliis  was  possibly  true  as  no 
“-iminoglutarate  was  used  as  a standard  for  identification. 

Organic  acids  from  seedlings  supplied  P2  and  contained  the 
most  c.  Here,  as  in  ethanol  extract  and  sugars,  incorporation 
of  14c  appears  to  be  influenced  more  by  P than  N.  Highest 
radioactivity  was  recorded  in  the  N^Pg  treatment  combination. 

In  amino  acids,  as  in  the  other  fractions,  14^;  fixation 
was  influenced  more  by  the  level  of  P than  N.  However,  the 
difference  is  much  less  pronounced  in  amino  acids.  The  apparent 
inciease  in  importance  of  N on  carbon  fixation  is  not  inter- 
pieted  as  indicating  an  extraordinary  relationship  between 
incorporation  and  .N’  but  rather  an  expression  of  the  requirement 
for  N in  amiino  acid  synthesis  via  am.ination  of  ketoacids 


74 


utilizing  carbon  derivatives.  Radioactivity  was  highest  in 
and  1^2  treatrnents  and  in  tlic  ^^2^1  ^urtilizer  regime, 

P appeals  to  be  a rate-limiting  element  in  pliotosyntlietic 
incorporation  of  carbon  in  sand  pine  grown  on  acid-washed  sand, 
it  had  its  most  pronounced  affects  on  the  fixation  of  carbon 
in  sugars,  the  principal  assimilate  and  translocate  in  sand  pine, 
and  presumably,  in  some  organic  acid  precursors  of  amino  acid 
synthesis . 

A N-P  ratio  of  1:2  produced  the  heaviest  seedlings,  a low 
green-nongreen  tissue  ratio,  and  the  highest  level  of  photoassimi lated 
C in  ethanol  extract  and  sugars.  Except  for  the  green-nongreen 
tissue  ratio,  the  most  beneficial  combination  of  N and  P included 
the  high  level  of  N (75.0  ppm)  and  the  high  level  of  P (150.0  ppm), 
i.e.,  the  N^p^  nutrient  regime  recommended  by  R.  H.  Brendemuehl 
(personal  communication) . The  green-nongreen  tissue  ratio  was 
most  nearly  balanced  using  the  same  ratio  of  N to  P.  Tlie  amount  of 
ladioactivity  in  the  amino  acid  fraction  of  green  tissue  extract 
was  slightly  higher  for  the  N2P2  than  the  N^Pj  regime.  In  organic 
acids,  N^P^  was  second  best  to  N2^P2- 

lliese  data  suggest  that,  of  the  treatments  used,  the  ratio  of 
one  part  N to  2 parts  P is  best  for  sand  pine  seedlings  on  infertile 
sands.  Furthermore,  they  suggest  that  procedures  involving 
assimilation  of  labelled  compounds  can  be  used  for  rapid  deter- 
mination of  optimum  nutrient  regimes  involving  more  than  just  two 


elements . 


75 


Biochemical  Pathways  Involved 

Tlie  highest  proportion  of  photoassimilated  was  contained 
in  the  sugar  fraction  of  the  ethanol  extract  from  green  tissue. 
Fructose,  glucose,  and  to  a lesser  extent  galactose,  contained 

i/irtually  all  tlie  labelled  caibon  in  sugars.  Organic  acids  contained 

14 

some  C principally  as  malic  acid.  Virtually  no  activity  was 
contained  in  the  amino  acid  fraction,  but  the  little  there  was, 
was  identified  as  components  leading  to,  and  involved  in,  the  urea 
cycle . 

Sugars  constitute  the  major  photosynthates  leading  to  forma- 
tion of  organic  and  amino  acids  and  eventually  to  protein  synthesis. 
'Ihese  data  suggested  that  the  glycolytic  pathway,  Calvin  cycle,  and 
the  tricarboxylic  acid  cycle  were  m.echanisms  for  interconversion 
of  these  compounds.  Furthermore,  they  suggested  that  activity  of 
key  enzymes  along  these  biochemical  pathways  might  provide  an 
index  of  superior  sand  pine  tree  growth. 

Objectives  of  the  final  phase  of  the  study  were  to  determine ; 

1)  whether  differences  exist  in  the  isoenzymes  of  glucose-6- 
phosphate  dehydrogenase  and  malate  dehydrogenase  and  in  proteins 
of  superior  and  nonsuperior  sand  pine  trees  and  their  half-sibling, 
seedling  progeny,  and  2)  if  the  soils  on  which  seedlings  were 
grov\'n  altered  their  morphology  or  the  migration  rate  and  activity 
of  isoenzymes  and  protein  bands. 

Seeds  collected  from  parent  superior  and  nonsuperior  sand 
pines  were  planted  in  Lakeland  and  Paola  sands.  Germination, 
num.ber  of  cotyledons,  and  foliar  color  were  recorded. 

The  protein  extract  from  green  tissue  of  parent  plants  and 
half-siblings  was  separated  by  gel  electrophoresis  then  stained 


76 


to  develop  isoenzymes  of  malate  dehydrogenase,  glucose-6-phosphate 
dehydrogenase  and  protein  bands.  Stained  gels  were  scanned  and 
measurements  were  made  of  the  number  and  Rf  value  of  bands  and  the 
intensity  of  densitometer  tracings. 

Measurement  of  glucose-6-phosphate  dehydrogenase  isoenzymes 
was  limited  to  the  3 bands  near  the  center  of  the  gels.  This 
limitation  was  caused  by  degredation  products  (Bakay  and  Nyhan, 
1969)  and  "nothing"  dehydrogenase  that  produced  false  bands;  and, 
protein  sulfhydryl  groups  (Dietz  and  Lubrano,  1967)  and  lightly 
stained,  unresolved  proteins  (Hall  et  al.,  1969)  that  caused  a 
foggy,  colored  background  at  both  extremes  of  the  gels.  Bakay 
and  Nyhan  interpreted  the  3 bands  as  subresolved  glucose-6- 
phosphate  dehydrogenase  isoenzyme  and  identified  them,  by  rate  of 
migration,  as  fast,  medium,  and  slow  components.  They  were 
treated  as  3 distinct  isoenzymes. 

Quantified  data  were  subjected  to  analysis  of  variance; 
selected  orthogonal  and  single-degree-of-freedom  comparisons 
were  made  of  soil  and  tree  treatment  main  effects  and  the  soil  x 
tree  interaction. 

Isoenzymes  and  proteins  bands  are  separate  entities.  Any 
one  can  act  as  a marker  indicating  genetic  variation  between 
superior  and  nonsuperior  trees.  The  Rf  and  activity  of  three 
glucose-6-phosphate  dehydrogenase  and  six  malate  dehydrogenase 
isoenzymes  and  the  Rf  and  staining  intensity  of  17  protein  bands 
were  examined.  To  obviate  repeated  qualification  to  differentiate 
between  isoenzyme  activity  and  protein  band  staining  intensity, 
the  term  "activity"  is  used  hereafter  with  both  isoenzymes  and 
protein  bands . 


77 


To  be  meaningful,  consistent  differences  have  to  exist  in 
tissue  of  superior  and  nonsuperior  trees  growing  on  the  same 
soil.  Two  individual  comparisons  differed  statistically,  but 
examination  of  the  data  showed  that  neither  was  consistent  for  all 
nonsuperior  trees.  For  example,  average  Rf's  for  glucose-6-phosphate 
dehydrogenase  isoenzymes  1,  2,  and  3,  were  significantly  higher  in 
superior  trees  than  in  nonsuperior  trees  labelled  D,  but  not  in 
nonsuperior  trees  A,  .6,  C,  and  E.  Statistically,  no  meaningful 
differences  were  found  among  parent  trees  or  among  their  progeny  for 
these  isoenzymes.  None  of  the  isoenzymes  studied  here  provided  an 
index  of  superiority. 

llie  only  indication  of  a possible  genetic  marker  was 
discovered  in  the  raw  data  (Appendix  Tables  9,  10,  and  11).  No 
protein  band  existed  between  Rf  0.29  and  0.39  in  superior  parent 
trees;  other  parent  trees  contained  at  least  one  band  within  this 
range.  The  marker  was  absent  among  siblings. 

The  Rf  and  activity  of  some  isoenzymes  and  protein  bands 
are  affected  by  the  soil  in  which  trees  grow  as  well  as  by  genetic 
factors.  In  some  instances,  both  the  band  and  the  controlling 
influence  can  be  identified.  Two  orthogonal  comparisons  were  made 
among  soils  irrespective  of  superiority  of  tissue  source.  'Fhe 
first  compared  results  obtained  from  Lakeland  (L)  with  that  from 
Paola  (P)  sand.  Half-sibling  seedling  tissue  w.as  used.  Since 
tissues  were  similar,  the  comparison  was  between  soils  developed  under 
thermic  (L)  and  hyperthermic  (P)  conditions.  Tlie  natural  range 
of  Ocala  sand  pine  is  limited  almost  exclusively  to  hyperthermic  soils. 


78 


In  this  comparison  the  significant  response  obtained  can  be 
attributed  to  soil. 

Hie  second  comparison  among  soils  measured  the  response  from 
half-sibling  seedlings  grouai  on  thermic  and  hypertliermic  sand 
(L+P)  with  that  from  parent  trees  growing  i?i  situ  (0,  for 
original  soils)  on  h)q5erthermic  sands.  The  significant  response 
obtained  can  be  attributed  to  genetic  factors,  half-sibling 
vs  parent,  or  to  age,  seedling  vs  grown  tree,  as  well  as  to  the 
soil.  Differences  in  age  were  discounted,  however,  because  only 
green  tissue  fi'om  the  current  year's  growth  was  used  and  because 
the  tissue  served  an  identical  function  involving  the  same 
enzymes  and  proteins  in  both  trees  and  seedlings. 

The  Rf  of  malate  dehydrogenase  isoenzymes  2,  3,  and  4 and  of 
protein  bands  12  and  16  were  significantly  higher  for  seedlings 
grown  in  L and  P than  for  parents  (0).  Rf's  in  the  L vs  P 
comparison  did  not  differ  significantly  suggesting  that  differences 
in  the  rate  of  migration  of  isoenzymes  2,  3,  and  4 and  of  protein 
bands  12  and  16  v/as  influenced  by  a combination  of  soil  and  genetic 
factors . 

.Activity  of  malate  dehydrogenase  isoenzymes  2 and  3 was 
significantly  higher  in  seedlings  grown  in  L than  P,  but  activity 
in  the  L+P  vs  0 comparison  did  not  differ  significantly.  This 
suggests’  that  their  activity  was  influenced  by  the  soil  more  than 
by  genetic  factors  or  else  the  parent-half  sibling  comparison 
would  also  have  been  significant.  Activity  of  protein  bands  7, 

12,  14,  16,  and  17  was  significantly  higher  in  L than  P.  Two 
of  these  bands,  12  and  16,  plus  three  additional  bands,  2,  9,  and 


79 


15  were  significantly  higher  in  the  L+P  vs  0 comparison.  This 
implies  that  activity  of  some  protein  bands,  o.g.,  12  and  16,  was 
influenced  by  soil  and  genetic  factors,  some  by  soil,  e.g.,  7, 

14,  and  17,  and  still  others  by  genetic  factors,  e.g.,  2,  9, 
and  15. 

Factors  believed  to  have  influenced  the  Rf  or  activity  of 
specific  isoenzpie  and  protein  bands  are  entered  under  "Remarks" 
in  Table  7 for  future  discussion. 

The  implication  that  the  soil  on  which  trees  grew  strongly 
influenced  the  Rf  and  activity  of  isoenzymes  and  proteins  was 
substantiated  by  comparisons  made  of  the  soil  x tree  interaction. 
Interpretation  of  results  summarized  in  Table  7 is  facilitated 
by  considering  separately  comparisons  made  under  columns  headed: 
Lakeland  vs  Paola,  Paola  vs  Original,  and  L vs  P+0  (Lakeland  vs 
Paola  plus  Original) . Isoenzymes  and  protein  bands  ^re  listed 
numerically  in  the  column  to  the  left  of  the  comparisons  according 
to  migration  rate;  1 was  fastest.  Consistency  among  superior  and 
among  nonsuperior  trees  was  essential  to  identify  genetic  markers 
and  to  provide  an  index  of  superiority.  It  was  also  essential 
to  substantiate  differences  attributable  to  soils,  genetic  factors, 
and  soil  plus  genetic  factors  suggested  by  the  comparisons  made 
among  soils. 

The  original  groupings  for  comparisons  in  the  soil  x tree 
interaction  were  made  to  determine  if  anticipated  differences  in 
isoenzymes  and  proteins  between  superior  and  nonsuperior  tissue 
could  be  detected  in  siblings  grown  on  soils  other  than  those  on 
which  the  parents  grew.  Here  they  serve  to  test  the  validity  of 
inferences  suggested  in  the  soils  com.parison. 


Table  7. --Comparisons  of  the  soil  x tree  interaction  showing  the  probability  of  a chance 
occurrence  and  the  soil  on  which  the  highest  values  were  obtained 


80 


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r-H 

<. / 

N— ' 

V / 

N— / 

< 

4c  4c 

4c 

4c 

4c 

4c 

4c 

4c 

4: 

4c 

4c 

+-> 

CQ  (D 

1-1  5^ 
r-»  CO 
< 

0) 

Ph 

p 

CO 


pjI 


* 

c o 
05  Z 
CQ 


£ 

<D 


UJ 

H 

O 

Pi 

P. 


ul 


cqI 


<1 


hJ  -3 

'w/  ' 

* 


■»«  ♦ 

•Jc  ^ 


*-J«^c-}e-lc4e^c^c-jc 


J h4 


♦ 

4: 


1^ 

•jc 


■): 


1-3 


hJ 

'w/ 

•jc 


hJ 

V—/ 

•je 


V / 

♦ 


hJ  J 

V / V / 

•Je  •)« 


•Jc 

•Jt 


•-4 

V y 

* 


h4  1-3  h4  m4 


♦ -Je  -Jc  4: 

4c  ■)«  4c 


^ J kJ 


4c  4t  * * 

4c  4c  4c 


h4 

4c 


*-3  iJ 


4c  4c 
4c 


h4 


4c  4c 
4c 


►J  hJ 


4c  4c 
4c  4c 


1-3 

4c 


1-4  k4 

V— / 

4c  4c 


(N^LOvOt^OOC^Oi-nCMtO^LONOr*^ 


+-> 

o 

< 


.-3 

V / 

4c 


in 

*t3 


oa 


4-1 

o 


o 

z 


83 


Paola  vs  Original  comparisons  were  made  on  sandy  soils  from 
the  sarr.e  general,  area.  For  this  reason  no  consistent  and  signifi- 
cant response  should  be  expected  in  the  Rf  or  activity  of  isoenzymes 
or  protein  bands  influenced  primarily  by  soil.  A response 
attributable  to  .genetic  factors  might  be  anticipated  in  appropriately 
labelled  bands  because  the  comparison  is  primarily  between  parent 
vs  half-sibling  progeny. 

Table  7 shews  that  the  labels  are  correct.  In  siblings,  Rf 
of  isoenzymes  2,,  3,  and  4,  and  of  protein  bands  12  and  16,  and 
the  activity  of  protein  bands  2,  4,  8,  12,  and  15,  and,  in  parents, 
activity  of  protein  band  6 were  highest  by  a statistically  signifi- 
cant degree.  Prxotein  bands  4,  6,  and  8 were  not  labelled,  but 
all  the  rest  bare  a genetic  or  a genetic  and  soil  designation. 
Conversely,  no  significance  was  recorded  for  the  activity  of 
malate  dehydrogemase  isoenzyme  2 and  3 or  protein  bands  7, 

14,  and  17,  influenced  by  soil,  or  of  band  16,  labelled  soil  and 
genetics.  The  only  exception  was  in  protein  band  9 which  bore  a 
genetic  label  but  exliibited  no  significant  oi'  consistent  response. 

A comparison  of  Lakeland  vs  Paola  plus  Original  was  made  to 
examine  differences  in  Rf  and  activity  of  isoenzymes  and  proteins 
attributable  to  "native  vs  non-native"  soils  in  superior  trees. 
Combining  the  data  from  Paola  and  Original  soils  also  introduced 
the  element  of  genetic  makeup,  lialf-sibling  vs  parent,  into  the 
comparison;  thus  it  is  not  surprising  that  mixed  results  were 
obtained.  Tlie  Rf  and  activity  of  many  labelled  and  unlabelled 
isoenzymes  and  proteins  exhibited  a significant  response.  In 


84 


every  instance  the  Rf  and  activity  were  highest  on  Lakeland 
sand . 

Comparisons  of  Lakeland  vs  Paola  examine  the  effect  of  a 
native  ;,md  non-native  soil  on  the  Rf  and  activity  of  isoenzymes 
and  protein  bands  in  progeny  from  superior  and  nonsuperior  trees. 
Individual  comparisons  were  made  for  1)  superior  trees,  2)  non- 
superior trees  collectively,  and  3)  nonsuperior  trees  bearing  a 
common,  identifying  letter.  Comparison  3 provides  a statistical 
breakdown  of  comparison  2 but  is  meaningless  by  itself. 

The  Rf  and  activity  of  all  significantly  affected  isoenzymes 
and  most  significantly  affected  protein  bands  in  the  3 compari- 
sons were  higher  on  Lakeland  than  Paola  sand  for  seedling  from 
superior  and  nonsuperior  parents  alike.  With  respect  to  soil, 
genetic  factors,  and  soil  plus  genetic  factors,  the  data  defy 
interpretation.  Had  the  effect  of  soil,  genetic  factors,  and  the 
combined  effect  of  soil  and  genetics  on  isoenzymes  and  protein 
bands  been  anticipated,  provision  could  have  been  made  to  clarify 
results  by  use  of  backcrossed  or  control-pollinated  stock  or 
possibly  rooted  cuttings  from  parents. 

It  is  tempting  and  sometimes  convenient  to  identify  protein 
bands  with  isoenzymes  that  I'eact  similarly  to  a given  stimulus  by 
direct  comparison  of  gels.  Both  are  protein.  Gabriel  and  Wang 
(1969)  successfully  accomplished  staining  for  both  protein  and 
enzyme  on  paired  gels  using  triphenyltetrazolium.  With  nitroblue 
tetrazolium  the  practice  does  not  appear  to  be  reliable.  Malate 
dehydrogenase  isoenzymes  2 and  3 reacted  similarly  to  protein 
bands  12  and  16  in  the  L vs  P and  L+P  vs  0 soils  comparisons, 


85 


yet  the  Rf's  of  the  isoenzymes  averaged  48. 7 and  37.4  ivhile  those 
of  the  protein  bands  averaged  40.3  and  24.8.  Possible  application 
of  this  method  was  further  tested  by  developing  ])rotein  bands  in 
gels  previously  stained  for  isoenzymes  and  then  comparing  these 
with  gels  stained  either  for  isoenzymes  or  protein  bands. 

Although  all  the  gels  had  been  processed  simultaneously  in  the 
same  electrophoresis  chamber,  the  position  of  the  bands  did  not 
coincide.  Development  of  isoenzymes  and  proteins  in  paired 
halves  of  gels  split  lengthwise  was  not  tried. 

A clue  to  deciphering  the  consistently  higli  response  to 
Lakeland  soil  in  Lakeland  vs  Paola  plus  Original  and  Lakeland  vs 
Paola  comparisons  was  sought  among  measurements  made  of  seedlings 
prior  to  harvest.  Seed  germination  vv’as  consistently  higher  on 
Paola  than  Lakeland  sand  (Figure  18).  'Hie  difference  might  be 
attributed  to  a response  to  origin  of  the  soils;  it  seems  more 
probable  that  it  reflects  the  influence  of  soil  texture  on  moisture 
available  for  imbibition  by  seeds  planted  at  the  surface.  Texture 
of  Lakeland  sand  was  coarse  while  that  of  Paola  sand  was  medium. 

No  genetic  variance  was  expected  because  seeds  were  from  the 
sam.e  trees,  and  samples  for  planting  were  selected  at  random. 

A comparison  of  cotyledon  numbers  (Table  8)  showed  no  meaningful 
differences  in  the  proportional  distribution  between  soils  or 
between  superior  and  nonsuperior  progeny.  There  was  no  apparent 
difference  in  size  of  cotyledons. 


Lakeland  Sand 


86 


+-> 

rt 

10 

(U 

0) 

+-> 

(U 


p: 

•H 

pH 

T5 


to 


P 

o 

<D 

Ph 

3 

10 

P 

o 

p 

T3 

P 

P 

P 

o w 

•H 

P 
P 
pH 

3 

(O 


S 

o 

P 

<p 

P 

o 


T3 

P 

+J 

P 

P 

bO 


to 
•H  P 
•M  T) 
P 

P W 


6 O 
P *H 
P +J 
bO  P 
o 

•3  O 
P fH 
P 

CO  LO 


00 


N0I1VNIWH3D  lN3D83d 


p 

P 

a 

•H 


A to 


87 


Table  8 . --Distribution  of  half-sibling  seedlings  possessing  3 to  7 
cotyledons 


PARENT 
TREE  LO- 


CATION 

AVERAGE 

OF 

NONSUPERIOR  TREES 

SUPERIOR 

TREE 

3 

4 

5 

6 

7 

3 

4 

5 

6 

LAKELAND 

SAND 

77 

0 

26 

66 

8 

0 

0 

4 

58 

38 

82 

0 

38 

52 

10 

0 

0 

48 

44 

8 

120 

0 

28 

56 

15 

1 

11 

44 

45 

0 

193 

1 

28 

54 

15 

1 

0 

41 

45 

14 

199 

2 

43 

53 

2 

0 

0 

30 

53 

17 

PAOLA  SAND 

77 

0 

28 

61 

10 

1 

0 

7 

64 

29 

82 

2 

30 

53 

15 

0 

0 

33 

59 

8 

120 

1 

34 

55 

10 

0 

0 

45 

48 

7 

193 

1 

23 

55 

21 

0 

0 

32 

61 

7 

199 

2 

42 

49 

7 

0 

0 

13 

60 

27 

7 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 


i 


88 


Color  of  the  foliage  '.vas  fairly  uniform  on  each  soil,  but  it 
differed  markedly  between  soils.  Color  differences  increased 
with  age  indicating  that  possibly  soil  aeration  and  moisture  in 
Lakeland  coarse  vs  Paola  medium  sand,  but  most  probably  the  availability 
of  nutrients  v;as  primarily  re:,ponsible . A comparison  of  colors 
was  made  shortly  before  harvest  against  standards  in  liunsell 
Color  Charts  for  Plant  Tissue.  It  showed  that  the  foliage  of 
seedlings  grown  on  Lakeland  sand  was  dark  greenish-yellow,  approxi- 
miately  7.5  GY  4/6  to  7.5  GY  5/6,  while  foliage  on  Paola  sand 
had  a lighter  hue,  2.5  GY  8/10  to  5 GY  7/8.  No  other  differences 
in  the  foliage  were  observed.  Some  fascicled  needles  developed 
on  all  seedlings,  and  the  needles  were  of  about  the  same  size. 

Ihese  data  raise  several  questions:  1)  What  characteristics 

of  the  soil  differ  sufficiently  to  alter  color  of  seedling 
foliage?  2)  Are  these  differences  in  any  way  related  to  the 
consistently  high  Rf  and  activity  of  isoenzymes  and  proteins 
observed  in  seedlings  raised  on  Lakeland  soil? 

Photosynthetic  rate  can  be  as  much  as  3 times  higher  in 
dark  green  than  light  green  leaves  (Kramer  and  Kozlowski,  1960). 

A corollary  that  serves  to  explain  the  consistently  higher 
activity  of  enzymes  and  proteins  on  Lakeland  than  Paola  sand  is 
that  the  darker  leaves  produced  more  substrate  for  protein 
synthesis  because  they  contained  more  chlorophyll.  Since  seedlings 
of  genetically  similar  origin  were  raised  under  identical  conditions 
except  for  the  soils,  differences  in  chlorophyll  content  are 
ascribed  to  available  nutrients  in  the  two  soils.  Hie  possibility 
exists  that  chlorophyll  formation  also  could  have  been  affected 


89 


by  a deficiency  or  an  excess  of  water  in  the  soils,  but, 

considering  the  slight  difference  in  texture  between  the 

sands,  and  the  care  with  which  seedlings  were  raised,  tlie  probability 

that  either  factor  played  a meaningful  role  seems  extremely 

remote . 

Table  2 showed  rhac  Lakeland  sand  contained  twice  as  much 
total  N,  considerably  more  Mg,  and  more  K than  Paola  sand.  N 
and  Mg  are  constituents,  of  chlorophyll;  a deficiency  of  either 
causes  chlorosis.  The  amount  of  N in  soil  is  a major  determinant 
of  leaf  protein  (Kynd  and  Noggle,  1945).  In  the  plant,  it  is 
an  element  essential  for  amino  acid  and  protein  synthesis. 
Conceivably,  the  divergence  in  N between  Lakeland  and  Pacla 
sand  could  have  modified  the  amino  acid  and  enzyme  components 
of  sand  pine  seedlings  growing  on  them  in  a manner  similar  to 
that  reported  in  slash  pine  seedling  tissue  following  addition 
of  N (Stanley  and  Smith,  1970),  i.e.,  by  altering  isoenzyme 
patterns.  In  this  respect  differences  in  available  Mg  could 
also  have  had  an  effect.  The  Mg  ion  is  also  a cofactor  in  many 
biochemical  reactions  including  conversion  of  glucose-6- 
phosphate  to  3-lactone  catalyzed  by  glucose-6-phosphate  dehydrogenase 
(Conn  and  Stumpf , 1964) , and  influences  the  reactivity  of  at 
least  one  glucose-6-phosphate  dehydrogenase  isoenzyme  in  some 
animals  (Hori  and  Matsui,  1967;  Hori,  Tsutom.u,  and  Matsui,  1967). 
Aside  from  the  difference  in  foliar  color,  no  apparent  syiTiptoms 
of  N or  Mg  deficiency  were  observed. 

The  K requirement  of  most  plants  is  liigh.  Bollard  (1955) 
'reported  that  dried  leaves  of  healthy  plants  contain  about  15,000 


90 


ppm.  Brendemuehl  (unpublished  data)  found  that  dried  needles  of 
Choctawhatchee  sand  pine  seedlings  grovm  in  a Lakeland  sand  with 
14  ppm  available  K contained  6,560  ppm  K.  So,  although  K accumulates 
in  needles  of  sand  pine  seedlings  against  a concentration  gradient, 
the  relatively  low  level  of  ; vailable  K in  the  Lakeland  and  Paola 
sands  of  this  study  suggests  that  the  sand  pine  seedlings  on  both 
soils  grew  at  suboptimum,  but  not  necessarily  deficient,  levels 
of  K.  Deficiency  symptoms  such  as  those  characterized  for 
foliage  of  white  pine  (Hacskaylo,  1962),  loblolly  pine  and 
V'irginia  pine  (Sucoff,  1961)  seedlings  were  not  apparent. 

Lakeland  sand  contained  slightly  less  available  Ca,  1/4  as 
much  available  P,  and  10  times  the  A1  of  Paola  sand.  Sucoff 
reported  no  deficiency  symptoms  in  loblolly  pines  supplied  with 
0.8  ppm  Ca  nor  in  Virginia  pines  raised  with  as  little  as 
0.2  ppm  Ca.  It  seems  unlikely,  therefore,  that  the  supply  of  Ca 
was  limiting  in  either  Paola  (44  ppm)  or  Lakeland  (30  ppm)  sand. 

No  deficiency  symptoms  were  evident. 

As  in  most  acid  sandhill  soils,  P availability  was  low.  Tliis 
was  especially  true  in  the  Lakeland  sand,  pH  5.6,  where  the 
presence  of  a comparatively  high  concentration  of  Al,  50.5  ppm, 
suggests  that  P was  fixed  as  the  insoluble  hydroxy-phosphate 
of  Al . Although  the  threshold  concentration  for  P deficiency  in 
Ocala  sand  pine  seedlings  is  unknowni  for  sandy  soils,  the  data 
suggest  that  it  may  lie  between  concentrations  found  on  Lakeland 
and  Paola  sand.  Seedlings  on  Lakeland  sand,  0.35  ppm  P,  evidenced 
the  dark  green  color  characteristic  of  a P deficiency  (Bonner 
and  Galston,  1952)  while  those  on  Paola  sand,  1.45  ppm  P,  did  not. 


91 


Tile  relatively  dai'k  green  color  of  seedlings  grown  on 
Lakeland  vs  Paola  soil  may  be  attributed  to  a P deficiency  and 
to  a greater  availability  of  N and  Mg.  Because  seedlings  were 
destroyed  during  preparation  of  acetone  powders  for  protein 
extraction,  foliar  analyses  could  not  be  made  to  corroborate 
suppositions  based  upon  foliar  color  and  the  soils'  available 
nutrient  content.  If  plants  were  deficient  in  P,  apparent 
conflict  exists. 

P is  essential  in  plant  metabolism.  Its  high-energy  bonds 
provide  a mechanism  for  stoi'age  and  energy  transfer  (Arnon, 

1953).  How,  then,  can  plants  growing  in  soil  containing  only 
0.35  ppm  of  available  P and  signalling  a P deficiency  symptom 
exhibit  high  protein  and  enzyme  activity  levels?  Lacking  cori'obora- 
tive  plant  tissue  analyses,  the  answer  can  only  be  conjectural. 

Two  possible  e.xplanations  follow. 

Tl;e  rate  of  P absorption  reaches  its  maximum  early  in  the 
growth  cycle;  at  a.  time  when  the  amount  absorbed  per  unit  of  growth 
is  higlier  than  at  later  stages  of  growth  (Dean  and  Fried,  1953). 

In  this  study  young  seedlings  were  used.  Tliey  could  have  absorbed 
enough  P during  their  first  month  or  so  of  existence  to  sustain 
a normal  metabolic  rate  for  about  a month.  In  the  interim, 
natural  recycling  of  P and  translocation  from  relatively  old  to 
meristematic  tissue  could  sustain  sufficient  sources  of  high 
energy  compounds  to  provide  tlie  increased  protein  synthesis 
ascribed  to  comparatively  high  levels  of  available  N and  Mg  found 


in  Lakeland  sand. 


92 

Plants  react  differently  to  a P deficiency.  Eaton  (1949, 

1950,  and  1952)  raised  sunflowers,  soybeans,  and  black  mustard 
plants  in  sand-solution  culture  with  and  without  P.  Analyses  of 
stem  tissue  extracts  showed  an  accumulation  of  carbohydrates  in 
ill  plants  but  a significant  increase  in  water-soluble  N, 
nitrate,  ammonia,  amino,  and  amide,  only  occurred  in  soybean. 
Accumulation  of  cai'bohydrates  and  nitrogen  is  symptomatic  of 
P deficiency  and  was  explained  by  interference  with  a)  protein 
synthesis  at  the  nitrate-reduction  stage  or  b)  protein  synthesis 
at  the  amide  stage. 

Sunflowers  were  grown  for  64  days  and,  according  to  Eaton, 
would  have  eventually  matured  under  P-deficiency  conditions, 
presumably  because  they  were  able  to  utilize  P of  complex 
organic  compounds,  'fhe  sand  pines  in  this  study  seemed  to 
react  similarly  to  sunflowers.  Under  field  conditions  both 
varieties  of  sand  pine  grow  to  maturity  on  P-deficient  soils. 

If  protein  synthesis  was  not  blocked  by  a P deficiency  in  the 
period  of  growth  studied,  then  differences  in  levels  of  N and  Mg 
could  account  for  the  consistently  higher  protein  and  enzyme 
activity  levels  found  in  seedlings  on  Lakeland  than  on  Paola  sand. 

A solution  to  the  apparent  dilemma  offers  opportunity  for 
further  investigation  into  the  differenctial  uptake  of  available 
nutrients  under  stress  conditions  imposed  by  deficiency  of  one 
or  more  nutrients,  as  related  to  the  affect  of  soil  and  plant 
nutrients  on  protein  production  and  enzyme  activity.  Hie  continued 
quest  for  a genetic  marker  and  index  of  superior  growth  using 
isoenzymes  affords  opportunities  for  future  investigations. 


93 

TTie  physiological  response  of  superior  tree  selection  to  soils 
and  soil  nutreint  levels  other  than  those  found  in  the  parent 
habitat  also  offers  opportunities  for  future  research. 


SUMMARY 


'ITiis  was  a study  of  sand  pine  growth  on  sandhill  soils.  It 
included  rneasuren'ents  of  the  affect  of  nutrient  levels  on 
fixation  of  photoassiniilated  and  comparisons  of  isoenzyme 
and  protein  migration  rates  and  activity  between  superior  and 
nonsuperior  trees  and  between  their  half-sibling,  seedling 
progeny  grown  on  Lakeland  and  Paola  sands. 

1.  Photoassimilation  of  ^^C02  in  a closed  system  and  at 
steady-state  conditions  is  directly  related  to  length  of 
exposure . 

2.  Translocation  of  ^^C-labelled  photos>nithate  from  green 
seedling  tissue  was  negligible  for  photoassimilation 
periods  of  10  min  or  less,  lliereafter,  the  proportion 

of  labelled  compounds  remaining  in  green  tissue  decreased 
in  relation  to  nongreen  tissue. 

3.  Young  Ocala  sand  pine  seedlings  did  not  incorporate  ^'^C02 
in  the  dark, 

4.  Chlorophyll  in  ethanol  extracts  decreased  the  efficiency 
a)id  tile  accuracy  of  liquid  scintillation  measurements. 

Both  were  improved  by  use  of  quenching  curves  and 
clarification  of  the  extract  with  powdered  activated 
charcoal.  Quenching  curves  were  unique  for  each  scintilla- 
tion counter, 

5.  Ihe  ethanol-soluble  fraction  of  green  tissue  contained 
most  of  the  photoassimilated  within  10  min.  Sugars 


94 


95 


contained  75%,  organic  acids  19%,  and  amino  acids  6%  of 
the  in  this  fraction. 

6.  N treatments  seemed  to  affect  chlorophyll  formation,  seedling 
growth,  and  the  photosyntlietic  incoi'poration  of  ^'^C. 

7.  P appeared  to  be  a rate- limiting  element  in  the  photos>Tithetic 
incorporation  of  C in  sugars  and  in  some  organic  acid 
precursors  of  amino  acids. 

8.  A N-P  ratio  of  1:2  in  complete  nutrient  solution 
produced  seedlings  with  a high  ratio  of  nongreen  to  green 
tissue  and  resulted  in  a high  level  of  incorporation  in 
sugars . 

9.  The  activity  and  Rf  values  of  malate  dehydrogenase  and 
glucose-6-phosphate  dehydrogenase  isoenzymes  did  not 
provide  an  index  for  rapid  growth  in  superior  Ocala 
sand  pine  tree  selections  or  in  their  seedling  progeny. 

10.  Absence  of  protein  bands  between  Rf  0.29  and  0.39  in 
superior  trees  was  the  only  indication  of  a genetic 
difference  between  superior  and  nonsuperior  parent 
trees.  This  genetic  marker  was  not  found  among  half- 
sibling, seedling  progeny. 

11.  Tlie  activity  and  Rf  of  som.e  malate  dehydrogenase  iso- 
enzyme and  protein  bands  were  affected  by  the  soil 

on  which  seedlings  were  grown  as  well  as  by  genetic 
factors . Both  the  bands  and  the  factors  influencing 


them  were  identified. 


96 

12.  Procedures  developed  in  this  study  may  be  applicable  to 
research  seeking  to  detect  genetic  aberrations  in  trees 
exhibiting  a superior  growth  rate  and  to  the  development 
of  optimum  levels  of  tree  nutrition. 


i 


APPENDIX 


" -> 


!-■  's^'l 


'•■■  ? 


\ 


98 


Table  9. --Protein  Rf  measurements  taken  from  half-sibling  seedlings 
grown  on  Lakeland  coarse  sand 


TREE 


Band 

A 

B 

C 

D 

E 

Super 

Rf  X 

100  -- 

1 

97 

95 

97 

95 

95 

96 

97 

97 

98 

98 

97 

97 

96 

93 

92 

91 

92 

92 

97 

98 

97 

00 

98 

98 

99 

99 

93 

96 

98 

98 

2 

00 

00 

00 

00 

00 

91 

92 

94 

93 

94 

93 

93 

90 

88 

87 

86 

87 

87 

94 

94 

94 

00 

93 

94 

93 

93 

00 

00 

92 

92 

3 

88 

88 

88 

87 

86 

00 

86 

87 

86 

87 

86 

86 

83 

82 

81 

79 

81 

81 

87 

88 

87 

00 

88 

87 

83 

83 

83 

87 

83 

82 

4 

82 

81 

82 

81 

81 

81 

82 

85 

84 

84 

83 

83 

80 

79 

77 

76 

78 

78 

84 

85 

84 

00 

84 

84 

78 

79 

79 

82 

78 

78 

5 

00 

00 

00 

00 

00 

00 

78 

81 

80 

78 

77 

78 

00 

00 

74 

73 

74 

7S 

81 

81 

80 

00 

00 

80 

73 

73 

72 

76 

72 

72 

6 

00 

00 

00 

00 

00 

00 

74 

78 

78 

75 

74 

76 

74  . 

73 

00 

00 

00 

72 

79 

79 

78 

00 

78 

78 

70 

70 

70 

73 

69 

69 

7 

00 

00 

00 

00 

00 

00 

70 

76 

75 

71 

71 

72 

71 

71 

69 

69 

69 

70 

77 

76 

76 

00 

76 

"'O 

67 

67 

00 

68 

64 

64 

99 


Table  9. --Continued 


TREE 


Band 

A 

B 

C 

D 

E 

Super . 

Rf  X 

100--- 

8 

69 

69 

70 

69 

69 

69 

00 

72 

72 

70 

66 

00 

69 

67 

66 

64 

66 

67 

73 

73 

73 

00 

72 

72 

63 

63 

63 

66 

62 

62 

9 

00 

64 

65 

64 

00 

00 

66 

68 

67 

67 

64 

66 

00 

63 

61 

58 

62 

62 

68 

69 

68 

00 

. 00 

68 

60 

60 

60 

63 

59 

59 

10 

00 

00 

00 

62 

64 

63 

60 

62 

61 

61 

61 

62 

62 

61 

59 

56 

60 

60 

66 

66 

66 

00 

66 

66 

54 

54 

54 

60 

53 

54 

11 

00 

00 

00 

00 

00 

00 

56 

58 

57 

57 

57 

00 

58 

57 

56 

53 

57 

57 

63 

63 

61 

00 

61 

62 

52 

52 

51 

53 

50 

49 

12 

00 

00 

00 

00 

00 

55 

52 

54 

53 

53 

52 

55 

51 

50 

49 

47 

50 

49 

56 

55 

55 

00 

55 

55 

45 

45 

45 

47 

44 

44 

13 

54 

54 

55 

44 

34 

34 

46 

48 

49 

49 

49 

51 

00 

00 

00 

00 

00 

45 

51 

49 

50 

00 

51 

51 

38 

39 

38 

41 

38 

38 

14 

43 

43 

44 

43 

43 

43 

00 

44 

47 

47 

47 

49 

43 

43 

41 

40 

42 

41 

49 

48 

47 

00 

48 

47 

00 

36 

35 

37 

34 

35 

100 


Table  9. --Continued 


TREE 


Band 

A 

B 

C 

D 

E 

Super 

Rf  X 

100 

15 

40 

40 

41 

40 

39 

40 

38 

41 

40 

41 

41 

42 

36 

36 

34 

32 

35 

35 

41 

41 

40 

00 

40 

40 

32 

32 

32 

34 

31 

31 

16 

00 

00 

35 

36 

35 

35 

32 

33 

33 

34 

34 

36 

28 

29 

28 

26 

28 

28 

34 

33 

32 

00 

33 

34 

26 

28 

27 

30 

26 

26 

17 

00 

00 

27 

26 

24 

25 

26 

27 

26 

28 

27 

31 

21 

21 

20 

18 

19 

19 

24 

25 

23 

00 

24 

24 

17 

18 

19 

20 

18 

18 

1 


101 


Table  10. --Protein  Rf  measurer^ents  taken  from  half-sibling  seedlings  grown 
on  Paola  sand 


TREE 


A 

B 

C 

D 

E 

Super . 

Rf  X 

100-  - 

95 

98 

98 

98 

98 

98 

97 

97 

97 

98 

98 

97 

93 

92 

92 

92 

93 

00 

97 

97 

99 

00 

97 

97 

00 

00 

00 

00 

98 

98 

88 

91 

89 

89 

90 

92 

93 

92 

92 

97 

93 

93 

88 

. 87 

87 

86 

88 

89 

93 

95 

93 

00 

91 

92 

92 

92 

92 

93 

90 

90 

00 

84 

00 

00 

00 

87 

86 

86 

82 

82 

00 

87 

82 

81 

81 

82 

81 

83 

86 

87 

86 

00 

85 

86 

83 

82 

82 

83 

88 

88 

82 

00 

84 

84 

83 

83 

83 

82 

75 

86 

84 

83 

00 

00 

79 

00 

78 

81 

83 

82 

82 

00 

82 

83 

78 

78 

77 

78 

81 

85 

00 

00 

00 

00 

00 

00 

76 

77 

00 

83 

77 

00 

78 

77 

78 

78 

00 

79 

00 

00 

00 

00 

00 

00 

72 

73 

72 

73 

80 

80 

00 

00 

00 

00 

00 

00 

74 

75 

71 

77 

72 

76 

00 

00 

00 

00 

74 

00 

77 

78 

78 

00 

77 

78 

70 

70 

69 

70 

78 

77 

102 


Table  10 . --Continued 


TREE 


Band 

A 

B 

C 

D 

1 on 

E 

Super 

7 

00 

00 

00 

00 

00 

00 

71 

71 

00 

00 

00 

00 

74 

72 

00 

75 

71 

00 

76 

76 

76 

00 

75 

76 

00 

65 

64 

65 

73 

73 

8 

71 

72 

71 

71 

72 

71 

00 

00 

00 

76 

65 

65 

72 

70 

71 

71 

00 

72 

72 

72 

73 

00 

71 

72 

64 

63 

62 

64 

61 

61 

9 

00 

65 

00 

00 

00 

00 

66 

64 

64 

65 

62 

61 

67 

66 

66 

67 

67 

62 

00 

00 

00 

00 

00 

00 

60 

60 

59 

61 

69 

68 

10 

64 

00 

63 

63 

64 

64 

61 

61 

61 

00 

00 

00 

61 

59 

.60 

00 

61 

60 

00 

65 

66 

00 

66 

65 

54 

55 

54 

55 

62 

57 

11  « 

00 

00 

00 

00 

00 

00 

57 

00 

57 

62 

00 

00 

58 

55 

56 

58 

58 

58 

62 

62 

62 

00 

61 

62 

51 

51 

50 

52 

58 

00 

12 

58 

59 

60 

60 

58 

58 

52 

54 

54 

61 

55 

55 

53 

51 

52 

54 

53 

54 

57 

57 

57 

00 

57 

57 

46 

48 

45 

47 

54 

53 

103 


Table  10. --Continued 


TREE 


Band 

A 

B 

C 

D 

1 nn 

E 

Super 

13 

55 

56 

55 

55 

55 

55 

48 

47 

47 

56 

48 

00 

00 

48 

49 

50 

51 

53 

54 

55 

00 

00 

00 

53 

00 

45 

00 

00 

52 

50 

14 

44 

52 

49 

49 

44 

45 

00 

00 

00 

00 

00 

00 

00 

00 

42 

45 

, 44 

51 

57 

48 

48 

00 

47 

46 

39 

35 

37 

40 

46 

45 

15 

00 

45 

44 

00 

00 

00 

40 

40 

41 

00 

41 

48 

32 

33 

34 

41 

36 

00 

39 

00 

00 

00 

00 

00 

31 

31 

30 

33 

36 

36 

16 

33 

34 

33 

44 

00 

34 

32 

00 

34 

49 

34 

42 

29 

25 

28 

37 

29 

38 

33 

40 

40 

00 

40 

41 

26 

27 

26 

29 

00 

00 

17 

24 

00 

27 

00 

26 

23 

00 

26 

00 

43 

00 

33 

00 

00 

00 

00 

00 

00 

27 

33 

34 

00 

32 

32 

18 

19 

22 

21 

28 

00 

104 


Table  11. --Protein  Rf  measurements  taken  from  parent  trees  growing  at  their 
original  locations. 


TRF.E 


Band 


B 

C 

D 

n 

Super 

Rf  X 

100--- 

— 

96 

97 

98 

97 

97 

96 

00 

98 

98 

98 

97 

97 

96 

98 

97 

95 

95 

97 

96 

98 

98 

98 

98 

98 

00 

00 

94 

00 

00 

00 

00 

95 

93 

95 

93 

93 

00 

92 

95 

94 

91 

92 

94 

93 

95 

94 

00 

94 

90 

91 

91 

91 

90 

91 

95 

00 

93 

00 

95 

00 

86 

87 

88 

88 

87 

90 

90 

88 

89 

89 

86 

87 

90 

90 

91. 

91 

90 

92 

86 

83 

88 

87 

87 

88 

91 

90 

90 

89 

90 

00 

81 

83 

83 

85 

82 

84 

86 

83 

84 

84 

82 

82 

00 

85 

86 

85 

85 

85 

00 

00 

00 

00 

00 

00 

81 

83 

81 

80 

82 

00 

75 

74 

75 

83 

75 

76 

79 

80 

75 

76 

73 

76 

80 

81 

80 

81 

81 

83 

81 

83 

82 

82 

82 

83 

76 

76 

00 

76 

76 

00 

68 

68 

69 

77 

68 

71 

71 

69 

70 

71 

68 

66 

76 

77 

77 

77 

79 

77 

00 

00 

00 

00 

00 

00 

71 

68 

69 

70 

70 

00 

105 


Table  11 . --Continued 


TREE 


Band 

A 

B 

C 

D 

1 nn 

E 

Super 

7 

00 

64 

64 

74 

00 

65 

68 

64 

66 

68 

66 

66 

69 

69 

69 

69 

69 

69 

73 

77 

74 

74 

76 

74 

63 

63 

00 

63 

64 

00 

8 

60 

00 

59 

69 

00 

00 

66 

58 

63 

66 

63 

64 

00 

64 

64 

67 

00 

68 

68 

69 

69 

68 

69 

69 

00 

00 

00 

00 

00 

00 

9 

56 

57 

56 

61 

61 

00 

61 

55 

58 

61 

59 

57 

63 

62 

61 

63 

64 

64 

00 

67 

67 

66 

67 

68 

00 

00 

00 

00 

00 

00 

10 

52 

52 

51 

58 

58 

58 

52 

51 

52 

53 

50 

52 

61 

61 

59 

58 

59 

60 

-- 

■ 62 

64 

64 

63 

66 

65 

00 

00 

00 

00 

00 

00 

11 

48 

48 

48 

54 

00 

54 

49 

48 

48 

50 

47 

00 

59 

60 

56 

57 

00 

59 

57 

58 

58 

59 

57 

58 

00 

00 

00 

58 

00 

00 

12 

00 

00 

46 

49 

49 

49 

43 

41 

42 

44 

41 

42 

54 

54 

53 

54 

00 

56 

00 

00 

00 

57 

00 

00 

00 

00 

00 

54 

00 

00 

106 


Table  11 . --Continued 


TREE 


Band 

A 

B 

C 

D 

E 

Super 

RF  X 

100 

13 

41 

42 

42 

42 

42 

00 

39 

37 

38 

40 

37 

39 

50 

47 

50 

53 

00 

00 

47 

48 

48 

47 

48 

49 

00 

00 

00 

47 

00 

00 

14 

00 

37 

39 

38 

37 

00 

36 

34 

35 

36 

34 

00 

45 

45 

44 

52 

52 

00 

44 

46 

46 

44 

45 

46 

44 

00 

00 

45 

00 

00 

15 

00 

35 

00 

00 

00 

00 

00 

29 

31 

00 

00 

00 

36 

38 

38 

49 

00 

00 

38 

37 

43 

38 

38 

41 

00 

00 

00 

00 

00 

00 

16 

00 

26 

00 

00 

00 

00 

28 

27 

28 

29 

26 

00 

35 

35 

34 

45 

46 

00 

29 

29 

37 

22 

30 

29 

00 

00 

00 

00 

00 

00 

17 

00 

21 

28 

00 

00 

00 

21 

20 

21 

23 

20 

22 

32 

32 

31 

38 

39 

00 

22 

23 

00 

00 

23 

23 

31 

00 

00 

00 

00 

00 

i 


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107 


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no 


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BIOGRAPHICAL  SKETCH 


Russell  MacBain  Burns  was  born  August  25,  1926,  at  New 
York,  New  York.  In  June,  1944,  he  was  graduated  from  Haaren 
High  School.  From  1944  until  1946  he  served  in  the  Infantry  of 
the  United  States  Army  in  Europe.  Following  his  discharge  from 
the  Army,  he  attended  the  Associated  Colleges  of  Upper  New 
York  and  Michigan  State  University  and,  in  1950,  received  his 
degree  of  Bachelor  of  Science  with  a major  in  Forest  Management. 

He  worked  for  the  Southern  Forest  Experiment  Station  of  the  U.S. 
Forest  Service  throughout  the  South,  and  while  stationed  at 
Oxford,  Mississippi,  attended  the  University  of  Mississippi. 

In  1959,  he  received  the  degree  of  Master  of  Science  with  a 
major  in  Biology  and  a minor  in  Mycology.  In  1966  he  was  selected 
by  the  Forest  Service  for  advanced  training  under  the  Government 
Employees  Training  Act  at  the  University  of  Florida.  The  Ph.D. 
degree  was  received  in  August  1971,  with  a major  in  Soils  and  a 
minor  in  Forest  Physiology. 

Russell  MacBain  Burns  is  married  to  the  former  Mildred  Ann 
Nastasia'and  is  the  father  of  three  children,  Stephen,  John,  and 
Russell.  Memberships  are  held  in  Sigma  Xi,  The  American  Society 
of  Plant  Physiologists,  Soil  Conservation  Society  of  America,  Society 
of  American  Foresters,  and  the  Florida  Academy  of  Science. 

i 


116 


I certify  tliat  I have  read  this  study  and  that  in  my 
opinion  it  conforms  to  acceptable  standards  of  scholarly 
presentation  and  is  fully  adequate,  in  scope  and  quality,  as 
a dissertation  for  the  degree  of  Doctor  of  Philosophy. 


August,  1971 


Chai] 

Professor,  Forest  Soils 


I certify  that  I have  read  this  study  and  that  in  my 
opinion  it  conforms  to  acceptable  standards  of  scholarly 
presentation  and  is  fully  adequate,  in  scope  and  quality,  as 
a dissertation  for  the  degree  of  Doctor  of  Philosophy. 


August,  1971 


Professor,  Forest  Physiologist 

I certify  that  1 have  read  this  study  and  that  in  my 
opinion  it  conforms  to  acceptable  standards  of  scholarly 
presentation  and  is  fully  adequate,  in  scope  and  quality,  as 
a dissertation  for  the  degree  of  Doctor  of  Philosophy. 


Robert  G.  Staley,  Co-jGHairman 


August,  1971 


Professor,  Soil  Physicist 


I certify  that  I have  read  this  study  and  that  in  my 
opinion  it  conforms  to  acceptable  standards  of  scholarly 
presentation  and  is  fully  adequate,  in  scope  and  quality,  as 
a dissertation  for  the  degree  of  Doctor  of  Philosophy. 


August,  1971  (‘4\  

Charles  C.  Hortenstine 
Associate  Professor,  Soil  Chemist 

I certify  that  I have  read  this  study  and  that  in  my 
opinion  it  conforms  to  acceptable  standards  of  scholarly  presentation 
and  is  fully  adequate,  in  scope  and  quality,  as  a dissertation 
for  the  degree  of  Doctor  of  Philosophy. 

jU 

Wayne  H.  Smith 

Associate  Professor,  Forester 


August,  1971 


I certify  that  I have  read  this  study  and  that  in  my 
opinion  it  conforms  to  acceptable  standards  of  scholarly 
presentation  and  is  fully  adequate,  in  scope  and  quality,  as 
a dissertation  for  the  degree  of  Doctor  of  Philosophy. 


August,  1971  /^/ 

Daniel  0.  Spinl^ 

Assistant  Dean,  So: 

I certify  that  I have  read  this  study  and  that  in  my 
opinion  it  conforms  to  acceptable  standards  of  scholarly 
presentation  and  is  fully  adequate,  in  scope  and  quality,  as 
a dissertation  for  the  degree  of  Doctor  of  Philosophy. 


August,  1971 


Rayji^ond  H . Brendemuehl 
Principal  Silviculturist,  U.S, 
Forest  Service 


This  dissertation  was  submitted  to  the  Dean  of  the 


College  of  Agriculture  and  to  the  Graduate  Council,  and  was 
accepted  as  partial  fulfillment  of  the  requirements  for  the 
degree  of  Doctor  of  Philosophy. 

August,  1971 


Dean,  Graduate  School