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Phycologia ( 1987) Volume 26 ( 1), 88-99
Seasonal growth and photoinhibition in
Plocamium cartilagineum (Rhodophyta)
off the Isle of Man
JO ANNA M. KAIN (JoNES)
Department of Marine Biology, University of Liverpool, Port Erin, Isle of Man, UK
J.M. KAIN (JONES). 1987. Seasonal growth and photoinhibition in Plocamium cartilagineum (Rhodophyta) off the Isle of Man. Phycologia 26: 88-99 .
Length frequency determinations in subtidal populations of Plocamium cartilagineum provided information on growth of upright thalli in relation to season and depth. At 2 m below lowest astronomical tide (LA T), under the laminarian canopy, growth started in March and was exponential until June, with a relative growth rate in weight of 0 .026 per day. Under wave exposed conditions few mature uprights survived into the following winter. In deeper water, under the laminarian canopy, growth was slower and deeper still (13-17 m) mature uprights survived throughout the year. Clearance of the phaeophycean canopy allowed faster growth over an 8 m depth range but in early summer appeared to reduce the growth at I m below LAT. Uprights held on blocks at 0.5 m below LAT and in tanks exposed to reduced mid-summer daylight grew more slowly than uprights receiving less irradiance. It seemed that 0.5 mmol m-2 S-l was inhibitory. These data agree with the concept of the species as 'shade loving', with a maximum relative growth rate which is slow compared with currently cultivated red algae but probably fairly typical of subtidal undergrowth species. At most depths, however, it is light limited for much of the year.
INTRODUCTION
In temperate waters the conditions that result
from seasonal changes vary considerably in their
favourableness for the growth of subtidal algae.
Some perennial species have become highly
adapted to the seasons so that they effectively
'anticipate' the favourable periods (e.g. Kain
1984). Annual and ephemeral species seem to
respond to these periods as the opportunity aris
es. Between these strategies is that of perennial
species which appear to respond to, but not 'an
ticipate', favourable growth conditions. Such a
species is Plocamium cartilagineum (Linnaeus)
Dixon.
Plocamium plants of various species perennate
in patches with creeping stolons (Shepherd 1981).
The upright portions that grow from these, while
clearly not separate plants, can be distinguished
as separate entities. The aim of this study was
to follow the growth of uprights of P. cartilagi
neum in relation to season, depth and the pres
ence of the phaeophycean canopy.
88
METHODS
Two sites were studied: the exposed (western)
side of Port Erin (Isle of Man, British Isles) break
water (54°5. 1'N; 4°46.2'W) at about 2 m below
lowest astronomical tide (LA T) and the steep
boulder bed below Spanish Head (54°3.3'N;
4°46.6'W) offering rock at a depth range down
to 17 m below LAT.
Plants were removed from the rock as gently
as possible, in order to avoid damage to the up
right portions. The best instrument for this is a
thumb-nail but wear is excessive. An artificial
nail was therefore cut from flexible PVC plate
and held on the thumb with a neoprene cap. On
each occasion plants were scraped systematically
from nine separate patches, transported in sep
arate net bags and stored in aerated seawater at
lO°C. In the laboratory, all the plants were ex
amined under a microscope. Provided that an
upright portion had an intact tip on what ap
peared to be the major axis and was attached to
a creeping portion or bore attachment discs at
Kain: Growth and photoinhibition in Plocamium 89
the base, it was cut just above the attachment
and the length measured. Thalli showing the
morphology of creeping portions, even without
attachment discs, and those of less than I cm
(when the morphology was indistinct) were ig
nored. Every eligible upright was measured in a
randomly chosen portion of each sample. Measurements were discontinued in August because
many of the larger uprights were damaged.
At Spanish Head canopy clearances were per
formed by cutting each canopy plant at the base
of the stipe. At I m below LAT the species re
moved were Alaria esculenta (Linnaeus) Gre
ville, Laminaria digitata (Hudson) Lamouroux
and L. hyperborea (Gunnerus) Foslie, at 5 m L.
hyperborea only and at 9 m L. hyperborea, Hal
idrys siliquosa (Linnaeus) Lyngbye and Desma
restia aculeata (Linnaeus) Lamouroux. The
cleared areas included several boulders or rocky
knolls at each depth; the control areas being sim
ilar undisturbed rocks on either side. Patches were
sampled at random within each area. In order to
avoid bias in selecting intact uprights for mea
surement, the samples of Plocamium from cleared
and control areas were processed in ignorance of
their origin.
In experiments on the exposure of Plocamium
to high irradiances, the length of each upright
was measured and a small piece of soft plastic
foam wrapped around its base. This was gripped
by a plastic tubing clip through the opening of
which a 5 mm hole had been drilled while it was
closed. The base of the clip embraced the barrel
of a 1 cm3 syringe which bore a numbered tag
and four of these clips as radial arms (Fig. 1).
When exposed in the sea the syringe barrel was
slipped onto a syringe plunger projecting through
an acetate sheet fixed to a concrete block. An
angle iron framework held a canopy of an acrylic
sheet with or without neutral filters over the
plants, with free access to water movement from
the slides. When exposed in tanks on land the
clip assemblies were first held in the laboratory
for 2 days in seawater containing 2.7 mg 1-I of germanium dioxide to inhibit diatom growth and
then placed in polyethylene mesh trays within
425 I polyethylene tanks containing filtered cir
culating seawater. These in tum were immersed
in a larger polyethylene tank through which sea
water recently pumped from the sea ran to waste,
as a crude form of temperature control. The tanks
were exposed to daylight through acrylic sheets
and neutral filters.
Fig. 1. The clip assemblage used for holding uprights of Plocamium on concrete blocks or in tanks.
Attempts to measure the reduction in light
caused by the laminarian canopy failed because
of the highly variable readings obtained.
Significance tests between samples of popu
lations were performed by using the 2 x 2 G-test
of independence (Sokal & Rohlf 1981) on the
proportion of the uprights which were more than
a selected length.
RESULTS
The patchiness of Plocamium on rocky surfaces
precluded sampling from a given area, without
incurring impossibly long diving times. The
length frequencies thus had to be calculated on
a percentage basis, rather than as plant density
on the rock. The disadvantage of this is that if
there is continuous recruitment of uprights, the
percentage of those in the larger size classes, pro
duced by growth, are diminished. The use of an
upper size limit, upper quartile, etc. for growth
determination was thus precluded. This difficulty
is well known to fisheries biologists so one of
their techniques was adopted.
The percentage frequencies in 5 mm length
classes on Port Erin breakwater in the Laminaria
hyperborea forest at 2 m below LAT at intervals
90 Phycologia, Vol. 26 ( I ), 1987
Length (em)
Fig. 2. Length frequency histograms of Plocamium uprights at 2 m below LAT on Port Erin breakwater between December 1 982 and August 1 983. Consecutively n was 1 89, 3 1 5,466,466,337,48 1 , 292,469, 426 and 360 C ... , identified mode; see text).
of a few weeks are shown in histogram form in
Fig. 2. In December 1982 there were few uprights
over 3.5 cm and it seems likely that these were
survivors from the previous summer. There was
little change by or during February, indicating
that little or no growth took place during mid
winter under the laminarian canopy. In mid
March, however, there was a departure from the
stepped reduction in frequency with length and
9 8 7
E 6
.c 5 '" c <U 4
-'
M A M
/e
A
Fig. 3. Mean modal triplet length plotted against time in 1 983.
the first appearance of a mode which probably
represented the group of young uprights making
the initial response to increased irradiance. This
was more apparent in April. (The May sample
may be anomalous: plants from three of the nine
sampled areas had to be discarded because ex
tended storage under aeration seemed to lead to
breaking.) It is likely that the lowest length class,
which was well represented up until June, in
cluded new recruits as well as non-growing up
rights, because most appeared young and healthy,
though in June a few appeared to be degenerat
ing. After June the lower length classes declined,
indicating a reduction in recruitment.
The mode which appeared in March can be
followed through to August (except in May) and
is marked with triangles in Fig. 2. Using the
'modal triplet' method of Menz & Bowers (1980),
the mean length of the uprights in the three length
classes spanning the mode on each occasion was
calculated and plotted against time on a semi
logarithmic presentation in Fig. 3. The anoma
lous May sample was omitted. It seemed that
growth was exponential until July and the cor
relation coefficient from the points from March
to July was 0.9997. The regression coefficient,
which is mathematically equivalent to the rela
tive growth rate in length (per day), was 0.0085.
An estimate of the relative growth in biomass
can be obtained from the double logarithmic plot
of fresh weight against length of Plocamium up
rights shown in Fig. 4. Here the slope of the GM
regression line (Ricker 1973) fitted to the data
covering the length range 3-7 cm was 3.11. The
relative growth rate in fresh weight can thus be
calculated as 0.026 per day, a doubling in 26
days. The GM regression fitted to all the data
had a steep slope of 3.86, indicating a change in
shape reflecting, presumably, the high degree of
branching in larger individuals. The linear growth
Kain: Growth and photoinhibition in Plocamium 9 1
•
I, ·"1 • •
• ... / •
. ": . , .. •• •
•
0.5 : ./ • •
en
:;:: en OJ 3 •
L '" �
u..
0.1
0.05
10
Length (em)
Fig. 4. Fresh weight of Plocamium uprights plotted against their length. Continuous line: GM regression for 3-7 cm (v = 3.1 1 ); dashed line, GM regression for all the data (v = 3.86).
rate between June and July samples was 0.55 mm
per day.
At Spanish Head populations of Plocamium
were sampled at 4 m depth intervals early in the
year. This site is washed by strong tidal streams
as well as being exposed to wave action. The size
frequency histograms are shown in Fig. 5. In Jan
uary/February 1984 at 1 m there was less pre
dominance of the shortest uprights than on Port
Erin breakwater at 2 m in 1983. A comparison
with the plants at 5 m seems to indicate that
some winter growth had taken place. It is pos
sible that the laminarian canopy at 1 m at this
site is thinner than on the breakwater. At 9 m,
there was a predominance of uprights of less than
3 cm, as at 5 m, but there were also a few very
long uprights. The two deepest populations,
however, showed a very different picture. At both
13 and 17 m there were uprights in all length
classes up to 13.5 cm.
A convenient measure of the upper spread of
20
10
% 10
5 10 Length (em)
1m
9m
13m
15
Fig. 5. Length frequency histograms of Plocamium uprights at various depths below LA T at Spanish Head around February. Dates of collection ( n in brackets): 1 m, 27 Jan. 1 984 (326); 5 m, 10 Feb. 1 984 (298);9 m, 27 Jan. and 1 0 Feb. 1984 (248); 13 m, 10 Feb. 1 984 (423); 1 7 m, 7 Mar. 1 983 and 27 Jan. 1 984 (410).
size frequency plots is the upper quartile. This
was determined for samples (including those
shown in Fig. 5) taken in early 1983 and 1984
at Spanish Head and is shown in Fig. 6. The
difference between the 1-9 m and the 13- 17 m
populations is again obvious. The drop from 1
to 5 m was presumably a result of growth in
shallow water but there was no further drop be
tween 5 and 9 m in either year, even if fertile (remaining from the previous year) plants were
eliminated from the calculation.
If the Laminaria canopy were limiting the light
supply to the undergrowth, the reduction of light
by the water column could be counteracted by
the reduction in canopy in deeper water (Kain
1971). In order to investigate this, areas were
cleared of canopy plants of Phaeophyceae at the
end of February 1984. These and control areas
were then sampled in April and June. The upper
quartiles are shown in Fig. 7 and significant dif
ferences in Table 1. Between February and April
there was a significant length increase in the vir
gin forest (control areas) only at I m. At 5 m
there was a significant increase in the cleared area
and both here and at I m the length was signif
icantly greater in cleared than in control in April.
At 9 m, however, there was no significant change
in length in either area between February and
92 Phycologia, Vol. 26 (I), 1987
E u
:E '" c � � t '" => cr � '" c. c. :::>
4
• • .. :::::-- . ----- ... .--...
/ /
/
10 15 Depth (m)
• /
Fig. 6. The upper quartile lengths of uprights of Plocarniurn at five depths below LAT at Spanish Head. .,7 Mar. 1 983; ... , 27 Jan. and 1 0 Feb. 1 984.
April. Between April and June, there was clear
growth in all areas and at each depth the plants
on the cleared areas were significantly different
from the controls, though at 1 m they were small
er instead of larger. The longest plants in June
were under the laminarian canopy at 1 m. The
only time when plants in cleared or control areas differed between 5 and 9 m was in cleared areas
sampled in April, when there were significantly
more larger uprights at 5 than at 9 m.
At 1 m depth at Spanish Head the greater length
of uprights under the canopy, compared with
those on the cleared area in June, could have
been due to a number of factors. One possibility
E
� '" c. c.
:::>
3 4 5 6 7 8 9 Depth (m)
Fig. 7. The upper quartile lengths of uprights of Plocarniurn at three depths below LA T at Spanish Head in 1 984. A, 27 Jan. and 10 Feb.;. 0, 10 and 26 April; .0, 1 9 June. Filled symbols, virgin forest; open symbols, phaeophycean canopy cleared in February.
Table 1. The significance (2 x 2 G-test of independence) of differences between the proportions of Plocarnium uprights over selected lengths in control and phaeophycean canopy cleared areas at different depths below LA T at Spanish Head in different months of 1 984. NS = not significant
More longer uprights: P�
In April than February: Control Cleared
1 m 0.00 1 0.001 5 m NS 0.05 9 m NS NS
In cleared than control: April June
1 m 0.025 (0.005 INVERSE)
5 m 0.025 0.005 9 m NS 0.025
At I m than 5 m:
Control 0.00 1 0.001 Cleared 0.00 1 NS
At I m than 9 m:
Control 0.001 0.00 1 Cleared 0.001 0.005
At 5 m than 9 m:
Control NS NS Cleared 0.00 1 NS
was that high light levels inhibited plants unpro
tected by the canopy. In order to test this, mea
sured uprights were exposed to daylight during
the same season the following year, 1985. They
were held on concrete blocks at 0.5 m below LAT
in sheltered water inside Port Erin breakwater
and covered with different densities of neutral
filters, or transparent acrylic sheet. The results
(Experiment I) are shown in Table 2. During the
6 weeks exposure all the plants in full daylight
were lost, while increasing numbers survived with
decreasing light. The mean relative growth rate
in length in 40% daylight, of 0.0086, was for
tuitously similar to that estimated from the Port
Erin breakwater population. It might appear from
Table 2 that there was clear cut evidence for light
inhibition on this experiment. However, in this
shallow sheltered site the new substrata provided
by the block assemblages were highly favourable
to filamentous diatoms and these covered all the
well lit surfaces including Plocamium uprights.
Beneath the 40% filter there were few diatoms.
These epiphytes could have caused or contrib
uted to the demise of the uprights exposed to the
higher irradiances. Two further experiments were
performed therefore. In these, uprights were held
in two tanks on land and exposed to two levels
Kain: Growth and photoinhibition in Plocamium 93
Table 2. The effect of various reductions of natural daylight on uprights of P/ocamium held in clips (Fig. I ) on concrete blocks in the sea (Experiment I) or in tanks on land (Experiments 2 and 3). In the calculation of relative growth rate in length (R L) plants which did not grow were included but not those which were lost or damaged
Experiment 3 Experiment I Experiment 2 1 2 July-
3 May-I 4 June 1 985 2-1 5 July 1 985 8 August 1 985 0.5 m below LAT Tanks Tanks
% of incident light 94 75 60 38 48 20 27 1 2 Estimated maximum irradiance 0.80 0.64 0. 5 1 0.32 0.9 1 0.38 0.50 0.22
(mmol m-2 s-')
Number of plants
Lost 40 38 22 6 1 4 1 6 3 5 Damaged 0 I 8 3 1 7 9 I I No growth 0 0 I 0 1 6 9 I 0 Growth 0 I 9 3 1 3 1 6 23 33
Relative growth rate
RL x 1 03 3.4 8.6 0.9 2.4 4.4 6.3 Significance of difference
P� 0.001 0.05 0.05
of daylight. The growth of diatoms was pre
vented by pretreating with germanium dioxide
and filtration of the circulating seawater medi
um. Full daylight was not used in either exper
iment because the plants were only just under
the water surface. In the sea, even at 0.5 m below
LAT, there is always at least 2 m of water within
2 h of mid-day off the Isle of Man. The results
(Experiments 2 and 3) are shown in Table 2. In
both experiments, growth was significantly faster
in the tank with lower irradiance. The hours of
sunlight were almost identical for the two pe
riods, yet there was lower growth at 20% in Ex
periment I than at 27% in Experiment 2. This
could have been due to inadequate temperature
control during the first period. It is not possible,
from these results, to designate a precise inhib
itory irradiance because of variation in natural
daylight and the times for which the plants were
exposed to the estimated maximum irradiance.
This could have been shorter in Experiment I than 2 or 3 because of the tidal height. It is ap
parent, however, that a maximum irradiance of 0.5 mmol m-2 s-' was inhibitory in both Ex
periments 1 and 3.
DISCUSSION
There is considerable evidence for frequent lim
itation of growth of Plocamium cartilagineum
by light. Uprights in the breakwater population
did not appear to grow during the darkest months.
At Spanish Head before April there was almost
no growth at 9 m below LA T and less at 5 than
I m. At all these depths clearance of the lami
narian canopy enhanced growth at some time.
On the other hand there is strong evidence for
inhibition by summer daylight in shallow water.
Plocamium has been described as a shade lover
(Boudouresque 1969, 1970) merely from the evi
dence of its habitat: this has now been confirmed
directly. It clearly can inhabit shallow water but
is found under a fairly dense canopy of lami
narians (Kain 1960; Smith 1967; Luning 1970)
and it can extend into deep water of more than
20 m (Kain 196 1; Norton 1968; Norton et al
1969). Inhibition of photosynthesis by high ir
radiance has been demonstrated in the Rhodo
phyta many times (e.g. Mathieson & Dawes 1974;
Mathieson & Norall 1975a, 1975b; King & Schramm 1976; Ramus & Rosenberg 1980). On
the other hand, photosynthesis of Plocamium
te/fairiae Harvey was still maximal at 40 k lux
(approximately 0.7 mmol m-2 s-') (Yokohama
1973) whereas in the present study growth was
clearly suboptimal when P. cartilagineum was
exposed to 0.5 mmol m-2 s-'. Inhibition of ac
tual growth of red algae seems to have been re
corded only by Boney & Comer ( 1962, 1963) in
sporelings of three species, by Jones & Dent ( 1971)
in sporelings of five species and by Polne et al
( 198 1) in adult Eucheuma.
The seasonal growth pattern of Plocamium
cartilagineum can be contrasted against those of
the seasonally highly adapted canopy-former
94 Phycologia, Vol. 26 (I), 1987
Laminaria hyperborea (Kain 1976) and two of
its fellow undergrowth species Delesseria san
guinea (Hudson) Lamouroux and Odonthalia
dentata (Linneaus) Lyngbye (Kain 1984). In the
latter, growth starts in mid-winter, in spite of
low irradiances, when nutrient levels are high.
The reason that the growth of Plocamium is de
layed until March is presumably because it lacks
stored materials and is reliant on photosynthesis.
The same may apply to Chondrus crispus Stack
house and Mastocarpus stellata (Stackhouse)
Guiry in the northwest Atlantic which show little
sign of growth before March (Mathieson & Burns
1975; Burns & Mathieson 1972). Tissue loss in
Plocamium is also different from plants such as
Delesseria. In the latter it occurs at a particular
time of year as part of a seasonal pattern (Kain
1984); in Plocamium the longer upright portions
may disappear in autumn if they are subjected
to wave action or they may be present all year
round in deeper water. A very different seasonal
strategy, with several cohorts arising each year,
is shown by Asparagopsis armata Harvey (Ar
anda et al 1984).
In species growing mainly at the apex one might
expect a linear rather than a logarithmic pattern.
The former has sometimes been observed in red
algae (Jones & Dent 1971; Bird et aI 1977; Simp
son & Shacklock 1979; Mumford 1979; Guiry
1984). On other occasions, clear logarithmic
growth has been maintained for days (Edwards
1977) or weeks (Waaland 1979; Polne et aI 1981).
As individual plants become larger and the pro
portion of growing tissue smaller it is surprising
to observe continued logarithmic growth as in
Plocamium on Port Erin breakwater. As the
species was probably light limited, the relative
reduction in growing tissue could have been
counteracted by increasing light until July (Kain
et al 1976). A further consideration may be per
tinent to explaining logarithmic growth. If light
were limiting then the rate of photosynthesis
rather than an upper limit to the rate of cell di
vision or expansion would have been limiting.
An increase in the number of photosynthetic cells
could then be the equivalent of an increase in
the number of growing cells, implicit in the con
cept of logarithmic growth. This, however, pre
supposes translocation of photosynthate, not yet
demonstrated for Plocamium or its near rela
tives . . In experiments on cultivation of red algae most
workers assume that growth is logarithmic because they quote the growth rate in per cent per
day (Yoneshigue-Braga & Baeta Neves 1981), as
doublings per day (Lapointe et al 1984; Fried
lander & Dawes 1984), as log2 weight change per
day (Bird et al 1979) or, in the sense of Evans
( 1972), as the relative growth rate (Morgan et al
1980; Morgan & Simpson 1981a, 1981b; Pat
wary & van der Meer 1983, 1984). This is un
derstandable when larger plants are cropped be
cause the proportion of growing tissue may
remain substantially constant.
There seems to be some confusion between
the relative growth rate R (or specific growth rate
JL) and percentage increase per unit time. The
formula for the former is sometimes used for the
latter (x 100) (DeBoer & Ryther 1977; Braud & Perez 1979; Rosenberg & Ramus 198 1; Rueness
& Tananger 1984; Fujita & Goldman 1985). An
example can illustrate the real difference. If a
plant weighs 100 g at the start of a 24-h period
and 120 g at the end, one might say that it had
grown 20%. The compound interest formula for
one payment per unit time:
% increase = 100 [ (::ft I]
would give this result. The compound interest
formula for continuous interest is mathemati
cally equivalent to 100 x the relative growth rate
formula:
In Wt - In Wo R = ----''----...::.
t
These would give values of 18.2% and 0. 182
day-I respectively. The discrepancy between the
results given by the two types of formula is great
er with larger and less with smaller values. As
algae grow more or less continuously it is clearly
preferable to use the latter formula and, to avoid
confusion, call it the relative growth rate, R
(Evans 1972).
For obvious reasons the relative growth rates
of economic red algae under cultivation have
been frequently measured and some are shown
in Table 3. Gracilaria tikvahiae, Hypnea mus
ciformis, Neoagardhiella baileyi and possibly
Devaleraea ramentosa are the fastest growing
species, each with a recorded R M of over 0. 15 per
day. Genera such as Iridaea, Eucheuma, Gelidi
um, Gracilaria, Palmaria and Chondrus contain
fairly fast growing species. None of these, of course, are deep subtidal 'shade loving' genera
or they would not have been chosen for culti
vation which requires 'sun plants' for high pro
duction rates. Waaland ( 1977), however, cul-
Kain: Growth and photoinhibition in Plocamium 95
Table 3. The maximum relative growth rate in length (R L) or weight (R M) per day of species of F1orideophyceae in tank, raft or rope culture. R calculated from percent increases when necessary. Ranked (using maxima and assuming RM � 2 X RL)
Species
Graci/aria tikvahiae McLachlan Gracilaria tikvahiae Graci/aria tikvahiae (mutant) Gracilaria tikvahiae Graci/aria tikvahiae Gracilaria tikvahiae Graci/aria tikvahiae (polyploid) Graci/aria tikvahiae Graci/aria tikvahiae Gracilaria tikvahiae Graci/aria tikvahiae Gracilaria tikvahiae Graci/aria tikvahiae Graci/aria tikvahiae Devaleraea ramentacea (Linnaeus) Guiry Hypnea musciformis (Wulfen) Lamouroux Hypnea musciformis Neoagardhiella bai/eyi (Kiitzing) Wynne et Taylor Neoagardhiella baileyi Neoagardhiella baileyi Gelidium sp. Gracilaria sjoestedtii Kylin Iridaea cordata (Turner) Bory Iridaea cordata I. cornucopiae Postels et Ruprecht I. heterocarpa Postels et Ruprecht Eucheuma unciatum Setchell et Gardner Gelidium coulteri Harvey Gracilaria edulis (Gmelin) Silva Gracilaria verrucosa (Hudson) Papenfuss Gracilaria verrucosa Palmaria palmata (Linnaeus) O. Kuntze Palmaria palmata Palmaria palmata Palmaria palmata Farlowia mollis (Harvey et Bailey) Farlow et Setchell Gracilaria exasperata Harvey et Bailey Gracilaria exasperata Gracilaria exasperata Chondrus crispus Chondrus crispus Chondrus crispus Chondrus crispus Gracilaria sp.
Plocamium cartilagineum Eucheuma spinosum (Linnaeus) J. Agardh Eucheuma spinosum Hypnea cervicornis J. Agardh H. nidifica J. Agardh Callophyllis jlabullata Harvey Gracilaria arcuata Zandard Hypnea chordacea Kiitzing Furcellaria lumbricalis (Hudson) Lamouroux Furcellaria lumbricalis Pterocladia caerulans (Kiitzing) Santelices Schizymenia pacifica (Kylin) Kylin Pterocladia capillacea (Gmelin) Bornet et Thuret Prionitis lanceolata (Harvey) Harvey
RM
0.35 0.25 0.22 0.20 0. 1 9 0. 1 9 0. 1 6 0. 1 5 0. 1 5 0. 1 3 0. 1 2 0. 1 2 0.078 0.05
0.097 0. 1 9 0. 1 0 0. 1 8 0. 1 7 0.058
0.072 0.090 0.090 0.037 0.083 0.078 0.077 0.076 0.076
0.096 0.052 0.083 0.077 0.059 0.057 0.065 0.080 0.053 0.035 0.074 0.066 0.025 0.004 0.058
0.039 0.052 0.024 0.039 0.036 0.035 0.035 0.032 0.030
0.0 1 7 0.023 0.0 1 7 0.0 1 6 0.0 1 0
Authors
Parker 1 982 Lapointe et al 1 984 Patwary & van der Meer 1 983 Bird et al 1 979 Edelstein et al 1 976 Fujita & Goldman 1 985 Patwary & van der Meer 1 984 DeBoer & Ryther 1 977 Fralick et al 1 98 1 DeBoer 1 979 Edelstein 1 977 DeBoer et al 1 978 Bird et al 1 977 Rosenberg & Ramus 1 98 1 Rueness & Tananger 1 984 Humm & Kreuzer 1 975 Haines 1 97 5 DeBoer et al 1 978 DeBoer & Ryther 1 97 7 Waaland 1 977 Rueness & Tananger 1 984 Hansen 1 983 Waaland 1 977 Waaland 1 98 1 Waaland 1 977 Waaland 1977 Polne et al 1 98 1 Hansen 1 980 Nelson et al 1 980 Rueness & Tananger 1 984 Jones 1 959 Morgan et al 1 980 Morgan & Simpson 1 98 1 a Morgan & Simpson 1 98 1 b Waaland 1 977 Waaland 1 977 Waaland 1 977 Waaland 1 98 1 Waaland 1 979 Bird et al 1 979 Simpson & Shacklock 1979 Braud & Delelpine 1 98 1 Bidwell et al 1 985 Y oneshigue-Braga & Baeta
Neves 1 98 1 Waaland 1 97 7 Braud & Perez 1 979 Soegiarto et al 1 977 Mshigeni 1 978 Mshigeni 1 978 Waaland 1 97 7 Nelson et a l 1 980 Mshigeni 1 978 Bird et al 1 979 Rueness & Tananger 1 984 Santelices 1 976 Waaland 1 977 Santelices 1 976 Waaland 1 977
96 Phycologia, Vol. 26 (1), 1987
Table 4. The maximum elongation rate per day (mm) or relative growth rate in length (RL), area (RA) or weight (R M) per day of species of Florideophyceae in the field. Ranked (approximately)
Species mm
Iridaea cordata Graci/aria tikvahiae Eucheurna acanthonoturn (Harvey) J. Agardh Plocarniurn cartilagineurn 0.55 Gelidiurn robusturn (Gardner) Hollenburg et
Abbott 0.63 Gelidiurn robusturn 0.35 Pterocladia capillacea 0.44 Eucheurna acanthonoturn Chondrus crisp us Calliarthron tuberculosurn (Postels et Ru-
precht) Dawson 0.10
tured some deeper water algae, including
Plocamium cartilagineum. This, with a rate of
0.039, grew faster in tanks, presumably under
optimal conditions, than observed in the sea in
the present study.
Field measurements of red algal growth rates
(Table 4) are much scarcer and, as one would
expect, the rates are slower than those under op
timum culture conditions. Apart from the fast
growing Iridaea and the slow growing coralline,
Calliarthron, they are remarkably similar to each
other.
Comparison of Plocamium growth rates with
other groups of macroalgae is difficult because
relative growth rates are rarely measured in whole
plants. Clearly its linear increase is slow: rhi
zomes of Caulerpa paspaloides (Bory) Greville
elongate at 10 mm per day (O'Neal & Prince
1982), Laminaria hyperborea sporophytes at 10.5
mm per day (Kain 1976), L. longissima Miyabe
at 68 mm per day (Sasaki 1969), Pelagophycus
porra (Leman) Setchell at 70 mm per day (Coyer
& Zaugg-Haglund 1982). Macrocystis integrifolia Bory at 95 mm per day (Lobban 1978), M. py
rifera (Linnaeus) C. Agardh at 140 mm per day
(Zimmerman & Kremer 1986) and Nereocystis
luetkeana (Mertens) Postels & Ruprecht also at
140 mm per day (Kain 1987).
Most of these, of course, are the faster growing,
large species in which linear growth 'would be
maximal. Smaller examples would be Fucus dis
tichus (Linnaeus) ssp. edentatus (de la Pylaie)
Powell with a rate of 0.36 mm per day (Strom
gren 1985) and F. spiralis Linnaeus with 0.42
mm per day (Schon beck & Norton 1979), both
slower than Plocamium in the summer.
When the spectacular linear growth rates of
the large algae are expressed in relative terms
RL RA RM Authors
0.088 Hansen 1977 0.075 Penniman et al 1986 0.04 Dawes et al1974
0.0085 0.026 This study Guzman del Proo & de la
Campa de Guzman 1979 Barilotti & Silverthorne 1972 Stromgren 1984
0.020 Dawes et al 1974 0.012 Taylor 1972
Johansen & Austin 1970
they seem quite slow, because of the small pro
portion of growing tissue. R in length (one third
of R in weight if there is no change in shape) of
juvenile Nereocystis stipes was 0.024 (Nicholson
1970) and of juvenile Macrocystis plants 0.031
(Dean & Jacobsen 1984). Fronds on mature plants
of M. pyrifera showed the highest value of about
0.08 (North 1971). A relative growth rate in
weight for a M. pyrifera 15 m frond can be cal
culated from a daily fresh weight production of
36 g per frond (Kain 1982) and a weight of 1.2
kg derived from the length/weight relationship
of 0.03 given by Jackson et al (1985): it is 0.03.
One has to go to an opportunistic species with
most of its cells capable of division for one of
the fastest relative growth rates: Viva lactuca
Linnaeus in laboratory culture had an R in the
area of 0.73 (Parker 1981).
The growth rates that have been quoted here
were all the maximum observed by each author,
to give an indication of the species' potential
under optimum conditions. Very young plants
were omitted. Clearly the relative growth rates
of embryos or sporelings can be considerably
faster. The variation in the observed relative
growth rates in plants of the same order of size
(Table 3) is likely to be due to different growth
potentials. The subtidal undergrowth 'shade lov
ing' species are presumably adapted to low light,
with low saturation levels and low maximum
photosynthesis rates. The result of the latter would
be low relative growth rates. This is clearly not
a strategy adopted by the whole of the division
when the relative growth rate of Gracilaria plants
can substantially exceed that of Macrocystis
fronds. If Plocamium is typical of the 'shade lov
ing' group the slow maximum growth rate is rare
ly a disadvantage: for most of the year the pop-
Kain: Growth and photo inhibition in Plocamium 97
ulations observed in this study appeared to be
limited by light.
ACKNOWLEDGMENTS
Michael Bates continued to give invaluable as
sistance underwater. I am also grateful to my
daughter, Bidda Jones, for help in the laboratory.
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Accepted 30 May 1986