J. Exp. Mar. Biol. Ecol., 154 (1991) 77-96
77
© 1991 Elsevier Science Publishers B.V. All rights reserved 0022-0981/91/$03.50
JEMBE 01685
Photosynthesis and growth of Nitzschia pungens f.
multiseries Hasle, a neurotoxin producing diatom
Youlian Pan ~, D u r v a s u l a V. Subba R a o
2
and Roderick E. W a m o c k
2
Ilnstitute of Oceanology, Academia Sinica, Qingdao, People's Republic of China; 2Biological Sciences Branch,
Department of Fisheries at~d Oceans, Bedford Institute of Oceanography, Dartmouth, Nova Scotia, Canada
(Received 23 April 1991; revision received 5 August 1991; accepted 10 August 1991)
Abstract: The pennate diatom Nitzschia pungens f. multiseries Hasle implicated in the amnesic shellfish
poisoning in bays of eastern Prince Edward Island, produces a neurotoxin, domoic acid. Batch cultures of
this diatom were grown at photosynthet,_'¢ photon flux densities (PPFD) of 1100 (high light, HL) and 105
(low light, LL) #mol m -2 s-~ at 10 °C. The relationships between photosynthesis and PPFD were
established on Days 1,4, 8, 15, 25 and 34 and were quantitatively described. Maximum specific growth rates
(#max) for the HL and LL cultures were 0.74 and 0.56 d a y - ~ respectively. Cells grown ~t HL had higher
assimilation number (Pmn: 2.2 #g C [#g Chl a] - ~ h - ~) but lower initial slopes (gn: 6.06 ng C [#g Chl a] I1- ! [#mol m - 2 s- t] --l)than those grown at LL (ProS: 1.7 #g C [#g Chl a] - i h - ~; 0ta: 8.69 ng C [#g Chl a] - i
h - ~ [#tool m - 2 s - ~] - ~). Both PmB and 0tn increased from Day 1 to Day 4, and then decreased as the cells
aged. Temporal variations in the rate of growth, cellular Chl a, cell concentration, carbon and nitrogen
showed differences in their magnitude and lag phase.
Key words: Age; Batch culture; Culture age; Growth; High light; Low light; Mass balance; Nitzschia
pungens f. muitiseries; Photosynthetic photon flux density (PPFD)
INTRODUCTION
Formation ofmonospecific blooms of marine diatoms is rarely known, as for example,
Asterionella japonica (Subba Rao, 1969), and production of any phycotoxin by such
diatom blooms was unknewn until 1987. Blooms of the pennate diatom Nitzschia
pungens f. mukiseries are unique because of the production of a neurotoxin, domoic acid,
the first toxin reported for any diatom (Subba Rao et al., 1988). Also, since 1987,
massive fall-winter blooms of this diatom have been associated with an annual outbreak
of amnesic shellfish poisoning (ASP) in Mytilus edulis L. which is cultured in Cardigan
Bay, eastern Prince Edward Island (PEI) (Subba Rao et al., 1988; Bates et al., 1989;
Addison & Stewart, 1989). Although the occurrence of domoic acid was initially limited
to eastern PEI, there is now evidence for its occurrence at low levels at coastal sites in
Nova Scotia and New Brunswick as well as on Georges Bank (Gilgan et al., 1990). This
Correspondence address: D.V. Subba Rao, Biological Sciences Branch, Department of Fisheries and
Oceans, Bedford Institute of Oceanography, PO Box 1006, Dartmouth, Nova Scotia B2Y 4A2, Canada.
78
Y. PAN ET AL.
is not surprising considering the ubiquitous distribution of the causative diatom
N. pungens f. multiseries (Subba Rao & Wohlgeschaffen, 1990). The resulting serious
commercial losses to the aquaculture industry and the loss of human lives due to the
eastern PEi incident in i987 prompted us to carry out physiological ecology studies,
similar to those on the toxic dinoflagellates Alexandrium tamarensis (Anderson, 1990),
Dinophysis norvegica (Dahl & Yndestad, 1985) and D. accuminata (Sampayo et ai.,
1990). In the Canadian Atlantic, especially in the Bay of Fundy, outbreaks of paralytic
shellfish poisoning (PS P) have been an annual event restricted to summer (White, 1989)
in contrast to the domoic acid problem which occurs in fall and winter.
Photosynthesis and growth are the two basic aspects in the overall physiology of
phytoplankton. A study ofthe relationship of photosynthesis and photosynthetic photon
flux density (PPFD, I) is essential to understand the physiological ecology of algae. In
both experimental and theoretical analyses of primary production of algae, several
investigators (Steele, 1962; Platt et al., 1975, 1980; and others) utilized the curvilinear
plots which relate the photosynthetic rates to the incident PPFD. Usually, Chl a and
particulate carbon are used as indices of biomass for normalizing photosynthetic rates.
Encouraged by our earlier studies (Platt & Subba Rao, 1970) we employed batch
cultures of N. pungens f. multiseries as analogues of natural blooms to understand the
physiological ecology of this toxin producing diatom. In this paper, we report variations
in measured and derived P - I parameters of N. pungens f. multiseries grown under two
levels of PPFD, at different phases of growth and the data are compared with other
pennate diatoms, winter algal blooms and toxic red water blooms.
MATERIALS AND METHODS
Nonaxenic clonal batch cultures of N. pungens f. multiseries isolated from Cardigan
Bay, PEI were grown in medium FE (Subba Rao et al., 1988), at 10-12 °C under
continuous cool white fluorescent light of 105 and 1100 #mol m - z s- 1. Cultures were
routinely grown at these two levels of PPFD and were subcultured every 5 days into
fresh medium for 10 days. For stock cultures, 500-ml flasks each containing 200 ml FE
medium were seeded with 25 ml of inoculum. At the beginning of the experiments, 3-1
Fernbach flasks containing 2 1of FE medium were seeded with 200 ml of exponentially
growing (5 days old) N. pungens f. multiseries adapted to the experimental PPFD which
was measured with a LICOR model Li-185B light meter. Cultures grown at 105 and
1100 #mol m - 2 s-~ were designated as low light (LL) and high light (HL) cultures
respectively.
Photosynthesis-PPFD (P-l) relationship was determined using the ~4C method
(Steemann-Nielsen, 1952) for cells harvested after 1, 4, 8, 15, 25, and 34 days growth
at 10°C. High specific activity ~4C-HCOf (111-222 C k Bq ml- ~ dependent on cell
density) was added to ~, 65 ml culture and after mixing thoroughly, 1-ml aliquots of the
culture were dispensed into 48 clean glass vials in a photosynthetron incubator and
PHOTOSYNTHESIS AND GROWTH OF NITZSCHIA PUNGENS
79
incubated for 30 min at different PPFDs ranging from 11 to 5000 #mol m - 2 s - 1 (Lewis
et al., 1985). Added activities were determined by adding 5 #1 of ~4C-labelled incubation
medium into 5 ml Aquasol scintillation fluid containing 10 #1 6N NaOH solution. The
incubation was terminated by adding 250 #l 6N HCI. The vials were shaken for > 1 h
to remove the residual HCO3- (Li & Goldman, 1981). A Beckman two channel
scintillation counter was used to determine the isotope activities. The relationship
between photosynthesis (P: #g C [#g Chl a ] - ~ h - ~ or #g C [#g C ] - ~ h - ~) and PPFD
(I" #mol m - 2 s - ! ) could be described by the photoinhibition model of Platt et al. (1980)
with the addition of a single parameter:
pB = [P~(1 - exp(-~BZ/Pp))exp(-flBl/p~)] + p~
(1)
In this formulation, P~ is the maximum potential photosynthesis in the absence of
photoinhibition; ~B (#g C [#g Chl a] - ~h - ~ [#mol m - 2 s - ~] - t or #g C [#g C] - ~h [#mol m - 2 s - ~ ] - a ) is the initial slope of P-I curve, that is photon efficiency, i.e.,
photosynthesis per unit PPFD, fib (same units as ~a) is the photoinhibition index and
Pda (same units as P) is the intercept of the P-I curve on the y axis. The additional
parameter Pda was found to be necessary to account for a background uptake of ~4C
in all samples. P~, P dB, ~B, fib were calculated by fitting Eqn. 1 into experimental data
points by non-linear regression using a commercial package employing the Marquardt
algorithm (Marquardt, 1963). All the points were equally weighted. The derived
parameters P~, Im, Ik, Is, were calculated from P~, ~B, fib following the relationship
among these parameters suggested by Platt et al. (1980).
Pma, the maximum biomass normalized photosynthetic rates:
( "B ) ( fib '~flll/~li
~B +
~B
(2)
lm, the PPFD corresponding to the maximum photosynthetic rate Pma:
im PB=s
ln(~B+flB)
0£B
fiB
(3)
4, =
(4)
Ik, photo-adaptive index:
Is, the P P F D corresponding to the maximumpotential photosynthetic rate in the absence
of photoinhibition:
ts = es/ B B
(5)
where, Ira, Ik, Is have the same units as (#mol m - 2 s - i ) .
Total carbon dioxide in the cultures was calculated from alkalinity determinations
(Strickland & Parsons, 1972) based on salinity determined with Guildline Salinometer
and pH with an Orion Research microprocessor ion-analyzer 901 at room temperature
(20 °C). Inorganic nitrate, phosphate and silicate concentrations in the medium were
measured with a Technicon Autoanalyzer II (Strickland & Parsons, 1972).
80
Y. PAN ET AL.
Biomass samples of the cultures were taken on 1, 4, 8, 15, 25 and 34 days. Cells were
enumerated on an l-ml aliquot settled in plankton chambers and counted using an
inverted microscope. Chl a determinations were based on duplicate samples employing
the fluorometric method (Strickland & Parsons, 1972), whereby cells retained on 25-mm
G F / F filters from 10-ml samples of cultures were transferred into vials containing 10 ml
of 90% acetone and refrigerated at 0 °C for 24-36 h before analysis. Particulate carbon
and nitrogen were analyzed using Perkin-Elmer 240B C H N Elemental Analyzer. Cells
from 40-ml samples of culture retained on 25-mm G F / F filters were dried at 60 °C
overnight and then rolled in silver filters for combustion (Strickland & Parsons, 1972).
The growth ofN. pungens f. multiseries in batch culture was found to be well described
by the growth model of Gompertz (Zwietering et al., 1990). When growth is defined in
terms of the logarithm of cell concentrations (or other biomass index) as a function of
time, changes in growth result in a sigmoidal curve such that there is a lag phase at
beginning (t - 0), tbllowed by an exponential phase ofgrowth and finally by a stationary
phase. The Gompertz equation may be expressed as:
y = a e x p ( - exp(b - ct))
(6)
where y = In (N/No), N is the cell concentration at different time of gro~eth, No is the
initial cell concentration, t is the time and the parameters a, b and c describe the shape
of the curve. Parameter a describes the asymptote (ln(N~/No), the maximum value of
y reached. The maximum growth rate (#m,,x) is given by ac/e, where e is the base of
Naperian logarithms (~2.718). The duration of the lag phase is given by ( b - l)/c
(Zwietering et ai., 1990). Growth curves as a function of time, normalized to cell
concentration and other biomass indices, were fitted by nonlinear regression. Growth
rates throughout the culture experiments were computed from the derivative of Eqn. 6
with respect to time:
dy/dt = ac e x p [ - exp(b - ct)] exp(b - ct)
(7)
using the parameter estimates obtained from nonlinear regression of Eqn. 6.
RESULTS
BIOMASS INDICES
Cell concentrations (in both low light (LL) and high light (HL) cultures) increased
exponentially for 8 days attaining a maximum concentration of 1.41-1.56 x 10s cells
1-~ by the 25th day (Fig. 1A). Subsequently, there was no marked change in cell
concentration in the stationary phase.
PHOTOSYNTHESIS AND GROWTH OF NITZSCHIA PUNGENS
,,#/,"'"°
10 8 I-
.T
10
81
~~
concentration
A: Cell
cJ
1
08
I
I
I
I
I
I
[
zx
,........-z~..............................................
~ ......................-~,
T
-
!00
¢1
B: Chlorophyll a
10
I
T
I
X
I
1
X
I000 -
o
E
/
"""
"l
1 O0
~ Particulat: carbon
""1
.
I
.........................
"
'~
~
I
.......................
"
.2
100 -
7
i--i
z
.~~
o
E
10
0
D: Particulate nitrogen
I
1
I
I
I
I
5
I0
I5
20
25
30
35
Culture age (days)
Fig. I. Growth curves based on different indices of biomass. Solid circles are experimental data for HL
culture, open triangles are experimental data for LL culture, solid lines are modelled values for HL cultu.,'e,
broken lines are modelled values, for LL culture (see text).
82
Y. PAN ET AL.
Chl a levels (Fig. 1B) were initially low (2.4 #g 1- ~in HL culture), despite the similar
cell concentrations in both HL and LL cultures (Fig. 1A). The HL cells contained less
Chl a than LL cells throughout the experiments (Fig. IB). As with cell concentration,
Chl a concentrations increased in a sigmoidal pattern with increasing age of the culture.
Maximum Chl a concentrations attained were 40.2 #g 1 - ' in the HL cukure and
103.3 #g 1- ' in the LL culture.
A sigmoidal increase in both particulate carbon and nitrogen over time also occurred
at both levels of PPFD (Fig. 1C,D). The principal features of interest are: (i)the
maximum concentrations of carbon in both HL and LL cultures were very close
(Fig. 1C); so were the maximum concentrations of nitrogen (Fig. ID); (ii) accumulation
of carbon, however, seemed to be more rapid than that of nitrogen (Fig. 1C,D); and
(iii) the lag phase for the accumulation of nitrogen seemed to be longer in HL cells
(Fig. 1D).
Of the three macronutrients, P O 4 and N O 2 + NO3 were abundant over the entire
34 days of growth (Table I). However, the initial levels of SiOa (84-86 #M) were
reduced to 11 and 8% in the HL and LL cultures, respectively, by Day 8 due to
utilization by diatoms for frustule formation. This feature corresponds with the onset
of the stationary phase. The decrease in silicate concentrations (Table I) between Days
1 and 15 was 72/aM (HL) and 73 #M (LL) and the corresponding increase in cell
concentrations was 1.0 x 10s cells 1 - ' and 1.14 x 10s cells 1-' (Fig. 1). Utilizing a
calculated cellular silicon of 20.2 pg cell- ' (HL) and 15.5 pg cell- t (LL), it is concluded
that the residual silicate (2.1-3.2/~M) available by Day 15 would be insufficient for
further division of cells.
Using Eqn. 7, growth rates (#) were calculated based on all indices of biomass.
However, because of the scarcity of data on the exponential phase, caution should be
TABLE I
Nutrient concentrations (#M) in culture media throughout experiment.
PPFD
(#mol in - 2 s - ' )
Growth time
(day)
SiO3
PO4
NO2 +NO3
1100
1
4
8
15
25
34
75.30
49.30
9.26
3.19
3.72
5.64
102.0
53.3
63.4
47.3
59.1
80.4
3028
3001
2961
2813
2892
2770
105
1
4
8
15
25
34
75.60
55.80
6.06
2.05
9.25
6.42
101.0
77.3
62.9
70.4
89.7
84.9
3085
2941
3032
2987
2937
2969
PHOTOSYNTHESIS AND GROWTH OF NITZSCHIA PUNGENS
83
applied when interpreting these values. The maximum growth rates (#max) based on cell
concentrations calculated from the derivative of Eqn. 6 for the HL culture was 0.56
day- ~with a lag phase of 1.07 days. The corresponding values for LL culture were 0.74
day- ~ and 1.85 days (Fig. 2A).
C ,8
-°,°°°°-..%
0.6
,,
%
.,
--
0.40.T2
",,,
A: Cell
concentration
"",
0.0
1.2
B: Chl r o p h y l l
0.9
a
0.6I
0.3-
"-'/'
0.0
l
.............
•
',
I-,
"=_j 0.4 -h
.:
O
""',,
C: C a r b o n
,j
0.2
0.4/
0.3+
0.2±
0.0
,
',
I
i
• •
0.1t- ""
.°-
0.0
0
3
6
Culture
9
12
5
age (days)
Fig. 2. Modelled growth rates (#, day- i)of different indices ofbiomass for first 15 days of culture. Solid
lines are of HL cultures, broken lines are of LL cultures.
84
Y. P A N E T AL.
Similar time-dependent variations in the accumulation rate of Chl a, particulate
carbon and nitrogen were observed. In the case of Chl a, the ,//max was 0.95 (LL) and
1.34 (HL) day- ' (Fig. 2B). The maximum growth rates based on Chl a was much higher
than those based on nitrogen. It occurred much earlier (Fig. 2B) compared to those
calculated for other biomass indices (Fig. 2A,C,D). The ~max for nitrogen was 0.2-0.3
(Fig. 2D), which was the lowest and the lag phase was the longest compared to the
others (Figs. 1D, 2D). During the early stages of growth, Chl a:Cell, Chl a:C and
500
400
A: C a r b o n
cJ
300
200
100
0
~,00
w
i
i
i
•
I
l
Ix
I
I
T
L
80i.
"
B:
N"t t r o g e n
~
60-
o
Z
~020. . . . . . . . . . -. . . . . . . . . . i . . . . . . . . . . . . . . . . . . . . . . . . . ~ . . . . . . . . . . . . . . . . . . . . . - ~
o
I
I
I
I
I
t
/\
T
C" C h l o r o p h y l l a
O
6'
L)
",
21 0
0
I
i
I
I
[
I
5
10
15
20
25
30
.35
Culture age (days)
Fig. 3. Variations with time ofcarbon (A), nitrogen (B), and Chl a (C) per cell. Solid circles are experimental
data for HL culture, open triangles are experimental data for LL culture, solid lines are modelled values
for HL culture, broken lines are modelled values for LL culture.
PHOTOSYNTHESIS
AND GROWTH
OF
NITZSCHIAPUNGENS
85
Chl a:N were all increasing. Ratios observed in the biomass indices seem to change
systematically with the age of the culture. Cellular carbon and nitrogen were at their
maximum on Day 1 and drastically decreased by Day 4 but exhibited no marked
differences between IlL and LL cells (Fig. 3A,B). Carbon:Chl a followed the same
pattern of decrease but was consistently lower in LL than in HL cells (Fig. 4A).
However, cellular Chl a in general, increased and reached a maximum after ~owth of
3.2-3.5 days and then decreased (Fig. 3C). The levels were always higher in LL cells
than in IlL cells. The C: N ratio in the cells ~bllowed a similar pattern, values peaked
by Day 4 in IlL and Day 8 in LL cells, followed by a gradual decrease (Fig. 4B).
A
• ,,.-i
o
700
600
°,,.,
A
..i.a
f,,,
500
,..,.
,,...
400
K.
-
o
o
.C
o
o
300
-
200
-
Q
I~,.
•
1 0 0 - /.
•
9
A
--,~. . . . . . . . . z~ . . . . . . . . . . . . . . . . 7< . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
I
0
t
- I
I
I
14
. ,,,,,d
E
o
---I
o
. ,...J
12
B
10
J
o
L
..,,=I
o
=o
,,o
~ " "°'"-4
:/ ~
............... " ......... i,,- ......................
®
4.
L
u
2
0
I
I
l
l
l
i
5
I0
15
20
25
50
55
Culture age (days)
Fig. 4. Changes with time in ratios of(A) carbon to Chl a by weight and (B) carbon to nitrogen by atom.
Solid circles are experimental data for HL culture, open triangles are experimental data for LL culture, solid
lines are modelled values for HL culture, broken lines are modelled values for LL culture.
86
Y. PAN ET AL.
PHOTOSYNTHETIC PARAMETERS
Photosynthesis-PPFD (P-I) curves exhibited reductions in photosynthetic rates at
high PPFDs ( > 1500 #tool m - 2 s - ~, Fig. 5) and so required an expression that included
a photoinhibition description. The empirical formulae of Platt et al. (1980) provided
with an additional parameter (a constant) describe our data quantitatively. Photosynthetic rates in our experiments were corrected for Pde because our data show that P~
varied significantly with the age of the culture: in exponentially growing cultures it was
< 10% of the maximum corrected photosynthesis (Pmn), in postexponential cultures, on
.5
,
:
"
'
T
!
T
iii..ii
~.l.
",'.5 T
~
I/.
|
::l.
.=.i,
o
o
~,
"",,
7
,.o)
~
"
•
'"::
" "'-.
o,s ~I!, .
......~-" . . . . . . . . . . .
~ ~ . . . . . . ~ .... ~----
~m
~i
eO
0 .0
A
A
A
.............
l[
~ "I
]
l
--
I
'I
"
0.06
0.05 i I
A°'"° ...A'-,~
H
I
-=
O.Oa
w
0.03
4
",,% A A
I
_.__1
w
0.02
e.4]
::L 0.0!
•
r~ 17,/,"
~ .....'.........
- . ' . ~
.,.
o.0o
,#
,'
I
0
1000
2000
,-~
30C0
I
4.000
Photosynthetic photon flux density (~mol m
5000
-2
s
-t)
Fig. 5. Relationships between photosynthesis and PPFD in cultures on 4 days growth. Solid circles are
experimental data for HL culture, open triangles are experimental data for LL culture, solid lines are
modelled values for HL culture, broken lines are modelled values for LL culture. (A) Normalized to Chl a
(#g C [#g Chla] - ~ h - ~); (B) Normalized to carbon (#g C [#g C]-n b-n).
PHOTOSYNTHESIS AND GROWTH OF NITZSCHIA PUNGENS
87
the other hand, it was 3 - 4 times higher than the corrected photosynthesis, similar to
the findings of Laws & Caperon ( 1 9 7 6 ) o n culture of a flagellate Monochrysis lutheri.
The photosynthetic response to P P F D varied systematically with the age of the
culture in both H L and LL cells. With increasing culture age, 0ca increased to attain a
m a x i m u m on Day 4 (6.06 ng C [#g Chl a] - ~ h - ~ [#mol m - 2 S - l ] - I at HL, 8.69 ng
C [#g Chl a] - ~h - ~ [#mol m - 2 S - l ] - i at LL; Fig. 6A), after which there was a drastic
decrease. The variations of Pma over time were similar to those of ~a, i.e., they attained
a m a x i m u m on Day 4 (2.2 Fg C [#g Chl a] - ~ h - ~ in H L 1.7 #g C [#g Chl a ] - i h in LL) and subsequently decreased (Fig. 7A).
T
"IT
"~
I
10
-o
8-.-
{
-
'=
6
,
}
,,,
i
,
A
Z1 ii;"...
~
".
",.-
i
i
":
em
.~.
2
0.30
T
!
I
T
0.25 -
I
I
0
13
0.20
/
•
o.!5
T
T
I
0.1o
:
T/
:'
0.00
± ..............
,
0
S
!0
j
j
15
20
,
25
30
35
C u l t u r e age (days)
Fig. 6. Variations of ~a in cultures of various phases of growth. Solid lines and circles are values of
HL culture, open triangles and broken lines are values of LL culture. (A) Normalized to Chla
(Fg C [#g Chla] -! h -~ [#molm-2s-~]-I); (B) Normalized to carbon (Fg C [#g C] -~ h -~
[Fmoi m- 2 s- i] - i).
88
Y. PAN ET AL.
2.5
T
-
2.0-
I
i
i---i
1.5-
m. i . o -
0.5
|
0.0
--I
I
0.06
T
0.05
z
:
:
o
e4)
B
,
1
_T'~ 0.04 ~
',
;
0.03-
~L
,
o 0.02~L
0.01 0.00
-
0
I
I
5
_
I
,
10
I
,
15
-7 ......
L . . . .
A
,
~
20
25
..
j
30
_
~5
Culture age (days)
Fig. 7. Variation of Pm
n in cultures of various phases of growth. Solid lines and circles are values of HL
culture, open triangles and broken lines are values of LL culture. (A) Normalized to Chl a (#g C [#g
Chl a] - i h - i ) ; (B) Normalized to carbon (#g C [#g C]- i h - l ) .
Interpretation of the P - I responses in HL and LL depends upon the biomass index
used (Fig. 5A,B). For example, if exponentially growing cells are normalized to Chl a,
HL cells achieve a greater maximum photosynthetic rate (Pm
n" assimilation number) than
the LL cells (2.2 compared to 1.7 #g C [#g Chl a ] - ~ h - ~; Figs. 5A, 7A). In contrast,
when normalized to cellular carbon, HL cells attain a Pma that is only 40~o of that of
LL cells (0.02 compared to 0.05 #g C [#g C ] - ~ h-~; Figs. 5B, 7B). This is a consequence of differences in the C'Chl a ratio in HL and LL cells. Irrespective of biomass
index chosen, HL cells attain P~ at a higher PPFD than LL cells (Im(HL)= 1272,
Im(LL) = 489 #tool m - 2 s - I, Table II). A similar result is seen with the photosynthetic
parameter describing the initial slope of P - I response (~B) which was of the same order
PHOTOSYNI'HESIS AND GROWTH OF N I T Z S C H I A P U N G E N S
89
TABLE II
Photoadaptive parameters of N. pungenr f. multiseries over time in cultures grown at two levels of PPFD
(/~molm - 2 s - ~).
PPFD
(#mol m - 2
Age
(days)
Im
[k
Is
II00
1
4
8
15
25
34
1006
1272
1716
1049
1086
593
172
415
399
217
244
156
212
569
427
239
346
154
105
!
4
8
15
25
34
599
489
379
197
426
276
86
140
102
35
114
46
311
339
134
31
106
42
S - I)
of magnitude both in HL and LL cells when normalized to Chl a (Fig. 6A). However,
in terms of cellular carbon, although the patterns were similar, the ~B in HL cells was
usually lower (Fig. 6B) because C : Chl a ratio was 3 times higher in HL cells (Fig. 4A).
The parameters Im, Ik and Is are independent of the biomass index chosen (Table II).
Consistent differences existed between the HL and LL cells. The Im of HL cells are
always higher (by a factor of 1.7-5.3) than those of LL cells; for Ik the factor is 2-6.2.
Ik seems to show similar changes to ~B, pmB and growth (Table II, Figs. 6, 7, 2).
DISCUSSION
The maximum photosynthetic rates attained on Day 4 of growth (Fig. 7) corresponds
to the end of the exponential phase based on Chl a and mid exponential phase based
on cell numbers, carbon and nitrogen. The Pn~ decreased as the cultures aged, which
is consistent with the findings of Humphrey & Subba Rao (1967) and Glover (1980).
The relative magnitudes of the maximum photosynthetic rate occurring during thc
exponential phase compared to that in the early stationary phase (P~ (Day 4): PmB (Day 8))
were 4.7 and 3.2 for HL and LL cells, respectively, which is similar to published values.
For example, for cultures of Thalassiosira pseudonana 3H, grown at 18 °C and 200
#mol m - 2 s - ~ (Glover, 1980), the corresponding ratio was 6. Our HL cultures yielded
higher assimilation numbers than those grown at PPFD an order of magnitude less,
consistent with the concept of light and shade populations (Falkowski, 1981).
The actual P - I values ofN. pungens f. multiseries differed from those transformed and
tabulated for other algae (Table III). The initial slopes ~B are low when normalized to
90
Y. P A N ET AL.
TABLE III
Summary of photosynthetic parameters of various algae.
Culture conditions
Taxa
Growth phase
°C
P'
L:D
10-12
1100
105
24L
]m
lk
ls
(/~moi m - 2 S - I )
Pennate diatoms
Nitzschia pungens f.
multiseries
Exp
Exp
Amphiprora paradoxa
10
30
10
140
12:!2
18
200
24L
569
339
Exp
Sta
27-57
Amphiprora kufferathii
18
400
24L
Exp
Sta
Fragilaria sp.
5-8
47
12:12
Exp
Cylindrotheca
closterium
20
23-27
800
86
237
24L
24L
24L
Navicula pelliculosa
415
140
106
95
Nitzschia delicatissima
(dominant sp. in
natural sampling)
Nitzschia atnericana
1272
489
Centric diatoms
Porosira pseudodenticulata
26-60
Thalassiosira scotia
28-50
Leptocylindrus danicus
I0
!0
12:12
9:i5
Dinoflagellates
Gonyaulax polyedra
330
12:!2
Exp
early Sta
late Sta
Ceratium lineatum
HL
LL
190
45
Ceratium fusus
HL
LL
325
190
Ceratium tripos
HL
LL
325
160
~ #mol m- 2 s - '
cell concentration; but are comparable to those of Nitzschia delicatissima (Erga, 1989)
and Nitzschia americana (Miller & Kamykowski, 1986b) when normalized with respect
to Chl a. The photosynthetic rates are also comparable when normalized to Chl a. When
normalized to carbon they are of the same magnitude as other pennate diatoms but are
PHOTOSYNTHESIS
AND GROWTH
an( • h - J (#mol m - -" s - i )- i )
cell - i
).017
).039
ng C pg Chi a - t
6.06
8.69
ng C pg C - i
0.06
0.26
pg C cell - ~
5.43
7.32
2.20
1.66
/,lg C/,/g C
0.021
0.049
!.2
!.7
0. !-0.5
0.28-1.30
39
21
!!-0.91
0.003-0.015
.2-9.2
50
5.8
8.7
Rivkin & Putt (1988)
0.01
0.006
4.9
2.0
0.083
2.76
3.8
1.3
2.32
2.92
Glover(1980)
2.3
Taguchi(1976)
Humphrey (1979)
Humphrey& Subba Rao
(1967)
Rivkin & Putt (1988)
Rivkin & Putt (1988)
70-172
29.6
21.9
Present study
Present study
Glover (1980)
74-276
.5-6.3
I
M i l l e r & Kamykowski
(1986a)
M i l l e r & Kamykowski
(1986b)
9.9-19
0.60
-
Erga (1989)
0.54-2.16
~2-2.22
75
pg C pg Chl a - I
91
Reference
P,~( • h - i )
11.28
17.84
~9-0.043
O F ¥1TZSCHIA PUNGENS
Verity (1981)
4.3
2.9
20.4
8.8
5.3
8.95
4.42
4.76
3.7
2.4
i.8
Prezelin & Matlick
(1983)
0.40
1.20
18.2
26.7
78
55
3.55
1.22
Rivkin & Voytek (1985)
0.40
0.48
11.4
9.6
130
90
3.71
1.80
Rivkin & Voytek (1985)
1.1
!.1
14.7
12.2
390
190
5.2
2.11
Rivkin & Voytek (1985)
low compared to Amphiprora paradoxa (Glover, 1980). Photosynthetic rates based on
particulate carbon are two orders of magnitude lower than other algae tabulated. The
carbon assimilation numbers for N. pungens f. multiseries are comparable with those for
some of the dinoflagellates summarized by Subba Rao (1988).
92
Y. PAN ET AL.
T
T
,.,.,,,
,--.,,,
2.5 i
I
4
2.0 ~
1
1.5 ~L)
::l.
B
,0
---
¢D
O
0.5-
15
.m
0.0
-
O
o
-0.5
0
:
I
I
!
I
2
3
4
Cellular
chlorophyll
5
a (pg cell -I)
Fig. 8. Relationship between photosynthetic rate ( p a ) and cellular Chl a. (A) Solid circles are values of i l L
culture: y = 0.98x - 0.27, r = 0.96; (B) open triangles are value of LL culture: y = 0.46x - 0.71, r = 0.87.
Number at each point denotes culture age (days).
The maximum carbon assimilation rates (#g C [#g Chl a ] - ' h - i ) are positively
correlated with cellular Chl a (Fig. 8, p < 0.01). The highest assimilation rates associated with the highest cellular Chl a were in the Day 4 cells and their lowest values were
in the advanced stationary cultures (34 days). Assimilation numbers increased between
Day 1 and Day 4 corresponding with a decrease in C : Chl a ratio. Following this, the
assimilation numbers decreased rapidly while the C: Chl a slightly increased and then
remained relatively constant in stationary phase (Figs. 7A, 4A). The pattern of changes
in assimilation numbers resembled that of C : N but with no strict correspondence
(Fig. 4B). This relationship of assimilation number (pB, #g C [#g Chl a ] - ' h - 1) to
carbon: Chl a or to cellular carbon : nitrogen for N. pungens f. multiseries also differed
from those for Leptocylindrus danicus (Verity, 1981) and could be attributed to the effects
of physiological stage of the cells. In N. pungens t. multiseries culture of 4 days growth,
assimilation number, C : Chl a ratio, N :Chl a increased with an increase in PPFD;
which is consistent with the observation on L. danicus (Verity, 1981).
Similar to the relationship between assimilation rate and cellular Chl a, the relationship between specific growth rate and cellular Chl a was positive (Fig. 9) and significant
(p < 0.01). The values were highest in exponentially growing cells and lowest in
advanced stationary phase cells (Fig. 9). Growth rate is also positively correlated to
assimilation rate (Fig. 10, p < 0.01).
08]
PHOTOSYNTHESIS AND GROWTH OF NITZSCHIA PUNGENS
93
4
A
0.6]-
4,
o o.'°
I
.°"
ooO°
B""
i
...-"
o.4
,,i
ID
•
Q
°°
°°°
.° .-""
0.2
"'"
o
2~
0.0-
A
n ?
•
0
2
Is
a
z~
,
,
,
i
i
i
i
1
2
~
4.
Cellular chlorophyll
,
a (pg cell
5
-I
)
Fig. 9. Relationship between specific growth rate and cellular Chl a. (A) Solid line and circles are values
of HL culture: 3' = 0.26x - 0.06, r = 0.94; (B)Broken line and open triangles are value of LL culture:
y = 0.2Ix - 0.32, r = 0.92. Number at each point denotes culture age (days).
0.8
A
.6
--
O
I
i
0.4-0.2--
O
L.,
r,..3
iO
0.0--0.2
i
-0.5
0.0
-
I
i
i
0.5
1.0
1.5
!
2.0
2.5
Photosynthetic rate (#~gC [#~g Chl a] -I h -i)
Fig. 10. Relationship between growth rate (#) and photosynthetic rate (pn). y = 0.23x + 0.06, r = 0.70,
solid circles are values of HL culture, open triangles are values of LL culture.
94
Y. PAN ET AL.
Comparison of growth rates based on the 4 biomass indices, i.e., Chl a, cell number,
carbon, and nitrogen showed that cell division was not internally consistent (Table IV).
In HL, Chl a-based growth rate increased and reached its maximum after 1.8 days
(Table IV). Cells were actively dividing as the photosynthetic capacity increased
resulting from the rapid increase of Chl a per unit volume (Figs. 1B, 2B) and reached
the maximum division rate after 3.5 days, i.e., 1.7 days later than Chl a based rate
TABLE IV
Maximum growth rates (#m.~x) and time it was reached (Tmax) based on cell concentration, Chl a, carbon
and nitrogen (based on growth model, Fig. 2), where HL and LL denote high and low PPFD cultures,
respectively.
Biomass parameters
Cell concentration
Chl a
Carbon
Nitrogen
HL
LL
~max
(day- l )
Tmax
(day)
~/max
(day- t )
~max
(day)
0.56
!.34
0.87
0.30
3.5
1.8
4.4
5.2
0.74
0.95
0.50
0.19
3.5
2.7
3.8
3.9
(Table IV). Particulate carbon reached its maximum growth by 4.4 days, followed by
particulate nitrogen that reached the maximum 5.2 days after incubation (Table IV).
The magnitudes of #max attained, based on the 4 biomass indices differed as well. In
LL culture, the maximum growth based on Chl a was attained after 2.7 days as
compared to 1.8 days at HL (Table IV). This could be due to variation in chemical
composition of algae as a function of growth rate. Shuter (1979) divided the cellular
carbon into four compartments and emphasized that differences in the flows of material
between compartments and between cells would result in unbalanced growth. Caperon
& Meyer (1972a,b) demonstrated that # based on ~4C, carbon or Chla cannot be
equated to the growth prediction based on nutrient uptake. Although similarities exist
between N. pungens f. multiseries and other diatoms (in the decrease of photosynthetic
rates as the cells aged, higher assimilation rate (Pro
B) and lower photosynthesis per unit
photon (~8) in HL culture than LL culture), there are obvious physiological differences
(such as the low Pm
n, 0~a).
Apparently unique to N. pungens f. multiseries is the production and intracellular
accumulation of domoic acid, particularly in the postexponential phase in F and FE
medium (Subba Rao et al., 1990) and later exponential phase in NH4 enriched medium
(Bates et al., 1990, presentation on the 2nd Canadian Workshop on Harmful Algae).
Usually, this occurs when the cells are metabolically inactive or when the cells are
physiologically stressed, i.e., photosynthetic rate, cellular materials and growth rate are
all decreasing. The unbalanced variation in cellular materials (Figs. 1, 2) and low
PHOTOSYNTHESIS AND GROWTH OF NITZSCHIA PUNGENS
95
photosynthetic rate (Fig. 7) may also be related to the production of the neurotoxin.
Reasons for such a timing of domoic acid production still need to be determined.
ACKNOWLEDGEMENTS
We are grateful to our colleagues K.H. Mann, J. Stewart, D. Gordon and W. K. W.
Li for criticism of the manuscript. We are thankful to T. Platt for the constructive
discussions of the P - I model. We thank Mark Hodgson for instructions on CHN
elemental analyses.
REFERENCES
Addison, R.F. & J'. E. Stewart, 1989. Domoic acid and the eastern Canadian molluscan shellfish industry.
Aquaculture, Vol. 77, pp. 263-269.
Anderson, D.M., 1990. Toxin variability in Alexandrium species. In, Toxic marine phytoplankton, edited by
E. Graneli et ai., Elsevier, New York, pp. 41-51.
Bates, S.S., C.J. Bird, A.S.W. deFreitas, R. Foxall, M.W. Gilgan, L.A. Hanic, G.E. Johnson, A.W.
McCulloch, P. Odense, R. Pocklington, M.A. Quilliam, P.G. Sire, J.C. Smith, D.V. Subba Rao, E. C. D.
Todd, J.A. Walter & J.L.C. Wright, 1989. Pennate diatom Nitzschiapungens as the primary source of
domoic acid, a toxin in shellfish from eastern Prince Edward Island, Canada. Can. J. Fish. Aquat. Sci.,
Vol. 46, pp. 1203-1215.
Caperon, J. & J. Meyer, 1972a. Nitrogen-limited growth of marine phytoplankton. I. Changes in population
characteristics with steady state growth rate. Deep Sea Res., Vol. 19, pp. 601-618.
Caperon, J. & J. Meyer, 1972b. Nitrogen-limited growth of marine phytoplankton. II. Uptake kinetics and
their role in nutrient limited growth of phytoplankton. Deep Sea Res., Vol. 19, pp. 619-632.
Dahl, E. & M. Yndestad, 1985. Diarrhetic shellfish poisoning (DSP) in Norway in the autumn 1984 related
to the occurrence of Dinophysis spp. In, Toxic dinoflagellates, edited by D.M. Anderson et al., Elsevier,
New York, pp. 495-500.
Erga, S.R., 1989. Ecological studies on the phytoplankton of Boknafjorden, western Norway. II Environmental control of photosynthesis. J. Plankton Res., Vol. 11, pp. 785-812.
Falkowski, P.G., 1981. Light-shade adaptation and assimilation numbers. J. Plankton Res., Vol. 2,
pp. 203-216.
Gilgan, M. W., B.G. Burns & G.J. Landry, 1990. Distribution and magnitude ofdomoic acid contamination
of shellfish in Atlantic Canada during 1988. In, Toxic marine phytoplankton, edited by E. Graneli et al.,
Elsevier, New York, pp. 413-417.
Glover, H.E., 1980. Assimilation number in cultures of marine phytoplankton. J. Plankton Res., Vol. 2,
pp. 69-79.
Humphrey, G.F., 1979. Photosynthetic characteristics of algae growth under constant illumination and
light-dark regimes. J. Exp. Mar. Biol. Ecol., Vol. 40, pp. 63-70.
Humphrey, G.F. & D.V. Subba Rao, 1967. Photosynthetic rate of the marine diatom Cylindrotheca
closterium. Aust. J. Mar. Freshwater Res., Vol. 18, pp. 123-127.
Lewis, M.R., R.E. Warnock, B. Irwin & T. Platt, 1985. Measuring photosynthetic spectra of natural
phytoplankton populations. J. Phycol., Voi. 21, pp. 310-315.
Li, W.K.W. & J.C. Goldman, 1981. Problems in estimating growth rates of marine phytoplankton from
short-term ~4C assays. Microb. Ecol., Vol. 7, pp. 113-121.
Marquardt, D.W., 1963. An algorithm for least-squares estimation of nonlinear parameters. J. Soc. Ind.
Appl. Math., Voi. 11, pp. 431-441.
Miller, R. L. & D. L. Kamykowski, 1986a. Effects of temperature, salinity, irradiance and diurnal periodicity
on growth and photosynthesis in the diatom Nitzschia americana: light-limited growth. J. Plankton Res.,
Vol. 8, pp. 215-228.
96
Y. PAN ET AL.
Miller, R. L. & D. L. Kamykowski, 1986b. Effects of temperature, salinity, irradiance and diurnal periodicity
on growth and photosynthesis in the diatom Nitzsch~a americana: light-saturated growth. J. Phycol.,
Vol. 22, pp. 339-348.
Platt, T., K.L. Denman & A.D. Jassby, 1975. The mathematical representation and prediction of phytoplankton productivity. Fish. Mar. Sere. Tech. Rep., No. 523, 110 pp.
Platt T., C.L. Gallegos & W.G. Harrison, 1980. Photoinhibition of photosynthesis in natural assemblages
of marine phytoplankton. J. Mar. Res., Vol. 38, pp. 687-701.
Platt, T. & D.V. Subba Rao, 1970. Primary production measurements on natural phytoplankton bloom.
J. Fish. Res. Board Can., Vol. 27, pp. 887-899.
Prezelin, B.B. & H.A. Matlick, 1983. Nutrient-dependent low-light adaptation in the dinoflagellate
Gonyaulax polyedra. Mar. BioL, Vol. 74, pp. 141-150.
Rivkin, R. B. & M. Putt, 1988. Seasonal pattern ofdiel periodicity in photosynthesis by polar phytoplankton:
species-species responses. J. Phycol., Vol. 24, pp. 369-376.
Rivkin, R.B. & M.A. Voytek, 1985. Photoadaptations of photosynthesis by dinoflagellates from natural
populations: a species approach. In, Toxic dinoflagellates, edited by D.M. Anderson et al., Elsevier, New
York, pp. 97-102.
Sampayo, M.A. de M., P. Alvito, S. Franca & I. Sousa, 1990. Dinophysis spp. toxicity and relation to
accompanying species. In, Toxic marine phytoplankton, edited by E. Graneli et al., Elsevier, New York,
pp. 215-220.
Shuter, B., 1979. A model of physiological adaptation in unicellular algae. J. Theor. Biol., Vol. 78,
pp. 519-552.
Steele, J.H., 1962. Environmental control of photosynthesis in the sea. Limnol. Oceanogr., Vol. 7,
pp. 137-150.
Steemann-Nieisen, E., 1952. The use of radioactive carbon ~4C for measuring organic production in the sea.
J. Cons. Perm. Int. Explor. Mer, Vol. 18, pp. 117-140.
Strickland, J. D. H. & T.R. Parsons, 1972. A practical Handbook of seawater analysis. Fish. Res. Bd Can.
Bull., Vol. 167.
Subba Rao, D.V., 1969. Asterionellajaponica bloom and discoloration off Waltair, Bay of Bengal. Limnol.
Oceanogr., Vol. 14, pp. 632-634.
Subba Rao, D.V., 1988. Species specific primary production measurements of arctic phytoplankton. Br.
Phycol. J., Vol. 23, pp. 273-282.
Subba Rao, D.V. & G. Wohlgeschaffen, 1990. Morphological variants of Nitzschia pungens Grunow f.
multiseries Hasle. Bot. Mar., Vol. 33, pp. 545-550.
Subba Rao, D.V., A. S.W. deFreitas, M. A. Quilliam, R. Pocklington & S.S. Bates, 1990. Rates of production of domoic acid, a neurotoxic amino acid in the pennate marine diatom Nitzschia pungens. In, Toxic
marine phytoplankton, edited by E. Graneli et al., Elsevier, New York, pp. 413-417.
Subba Rao, D. V., M. A. Quilliam & R. Pocklington, 1988. Domoic acid- a neurotoxic amino acid produced
by the marine diatom Nitzschia pungens in culture. Can. J. Fish. Aquat. Sci., Vol. 45, pp. 2076-2079.
Taguchi, S., 1976. Relationship between photosynthesis and cell size of marine diatom. J. Phycol., Vol. 12,
pp. 185-189.
Verity, P.G., 1981. Effects of temperature, irradiance, and daylength on the marine diatom Leptocylindrus
danicus Cleve. I. Photosynthesis and cellular composition. J. Exp. Mar. Biol. Ecol., Vol. 55, pp. 79-91.
White A.W., O. Fukuhara & M. Anraku, 1989. Mortality of larvae from eating toxic dinoflagellates or
zooplankton containing dinoflagellate toxin. In, Red tides - Biology, environmental science, and toxicology,
edited by T. Okaichi et al., Elsevier, New York, pp. 395-398.
Zwietering, M.H., I. Jongenburger, F.M. Rombouts & K. van 't Riet, 1990. Modelling of the bacterial
growth curve. Appl. Environ. Microb., Vol. 56, pp. 1875-1881.