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Lockdown musings on scurvy grass (Lepidium oleraceum)

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Abstract and Figures

1
Brief observations of vegetation following a  re on Flagstaff , Dunedin
John Barkla (mjbarkla@xtra.co.nz)
On Monday 16 September 2019 a  re swept through c. 30 ha of montane tussock-
shrub/ axland on the popular Pineapple Track that traverses Flagsta (668 m) above
Dunedin. Billowing smoke and  ames were clearly evident from the city and it took
eight helicopters and 35  remen to contain the  re. Dampening down continued
through Tuesday, and surveillance of hot spots was ongoing for several days.  e
Pineapple Track was closed for a week.
Evidence from sub-fossil logs suggests there was a cover of montane forest on Flagsta
until about 1300 AD. Chionochloa rigida-dominant tussocklands are thought to have
been present since at least the mid 19th century and maintained by periodic  res
(Wardle & Mark 1956). A hot spring  re in late 1976 burnt c. 100 ha. Given its close
proximity to Dunedin, the area around Flagsta has been a convenient research site
for investigating the e ects of  re on snow tussock, e.g. Gitay et al. (1991).
I walked through the burn site on 28 September, almost two weeks a er the  re
started (Fig. 1). As expected, it was a scene of blackened devastation (Figs. 2 & 3) with
bare charred rocky ground punctuated by tussock and  ax stumps and burnt stems of
exotic broom and native shrubs.
Figure 1 (top). View east towards Dunedin over south-facing burnt slopes, September 2019.
Figure 2 (above le ). A bare charred tussock- ax-shrubland, September 2019.
Figure 3 (above right). Burnt  ax, September 2019.
NO. 198
May 2020
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NEW ZEALAND
PLANT OF THE MONTH, p. 3
Poa antipoda. Photo: Rowan
Hindmarsh-Walls
TRILEPIDEA
Newsletter of the New Zealand Plant Conservation Network
2
I returned to the burn site on 25 April 2020, some seven months or one growing season later (Fig 4).
Mountain ax or wharariki (Phormium cookianum) has universally survived and vigorous regrowth
was clear (Fig 5). Some snow tussocks have perished but the majority have survived, as evidenced by
modest new tiller growth. Near the lower altitude margins of the burn some native shrubs, especially
Olearia arborescens, have resprouted extensively from their bases (Fig 6).
Figure 4 (top). View east towards Dunedin over south-facing burnt slopes, April 2020.
Figure 5 (above le). Recovering ax, April 2020.
Figure 6 (above right). Tussock hawkweed with basal resprout of Olearia arborescens behind, April 2020.
Much of the previously burnt bare ground has been colonised by a range of native and exotic plants.
Common native species include mountain astelia (Astelia nervosa), prickly shield fern (Polystichum
vestitum), mountain kiokio (Blechnum montanum), and alpine clubmoss (Lycopodium fastigiatum).
Common exotics include a range of pasture grasses, especially browntop (Agrostis capillaris) and sweet
vernal (Anthoxanthum odoratum), catsear (Hypochaeris radicata), tussock hawkweed (Hieracium
lepidulum), and swathes of seedling exotic broom (Cytisus scoparius) and gorse (Ulex europaeus). Burnt
tussock stumps in particular seem to be favoured establishment sites for wild broom seedlings.
ere are encouraging signs of recovery of native species, including some structural dominants, and it
seems inevitable that the vegetation will rapidly transition towards its pre-burn state. at vegetation,
without intervention, is likely to include a signicant and increasing component of woody weeds such
as exotic broom and gorse.
References
Gitay H, Wilson JB, Lee WG, Allen RB 1991. Chionochloa rigida tussocks 13 years aer spring and autumn re, Flagsta,
New Zealand. New Zealand Journal of Botany 29: 459–462.
Wardle, P & Mark, A. 1956. Vegetation and Climate in the Dunedin District. Transactions of the Royal Society of New
Zealand 84: 33.
Figure 7. Exotic broom seedlings established on burnt
tussock stump, April 2020.
3
PLANT OF THE MONTH – POA ANTIPODA
Rowan Hindmarsh-Walls
The plant of the month for May is the sub-antarctic grass, Poa antipoda, one of about seven
species of native Poa found in the New Zealand sub-antarctic region. The species is found on
Auckland, Campbell and Antipodes Islands, as well as Herekopere Island o Rakiura.
Poa antipoda, Falla Peninsula, Auckland Island, January 2020; (le) growth habit, (right) inorescence.
Poa antipoda typically occurs on clis and rocky outcrops, both on the coast and inland. It prefers
damp places, often within the dripline at the bottom of blus. The species is moderate in size
and bright yellow-green with soft, at leaves. The owering culms are usually open, with 3–4
owered spikelets that are green with pinkish-red tips. Like other Poa species, Poa antipoda has
soft membranous ligules.
This species is somewhat similar to a few of the other sub-antarctic Poa, namely P. foliosa, P.
ramosissima and P. tennantiana. P. foliosa diers from P. antipoda by being more robust and much
larger in size (up to 1.5 m compared to 20–60cm). P. ramosissima has lacerate ligules while P.
antipoda has entire ligules and P. tennantiana has plants that are stout and sti-leaved, unlike the
soft drooping leaves of Poa antipoda.
Poa antipoda is endemic to the New Zealand region and has a threat ranking of “At Risk –
Naturally Uncommon” due to its restricted distribution in the New Zealand sub-antarctic region.
On some of the sub-antarctic islands, the species is possibly threatened by competition with
exotic grass and herb species. On Auckland Island, seed predation by mice is a potential factor
limiting its spread.
The name Poa is the Greek word for meadow-grass or fodder. The species epithet antipoda means
Antipodean, of the Antipodes Islands.
You can view the NZPCN website factsheets for Poa antipoda at:
https://www.nzpcn.org.nz/ora/species/poa-antipoda/
4
Lockdown musings on scurvy grass (Lepidium oleraceum)
Peter J. de Lange (pdelange@unitec.ac.nz), School of Environmental & Animal Sciences, Unitec Institute
of Technology, Auckland
In the dim dark days when we still had Standards and Forms in New Zealand schools, my Standard 4
class studied Captain James Cook (1728–1779) and aspects of his ‘discovery’ of Aotearoa / New
Zealand. My memory of the lessons, some 43 years later is of course vague but I do recollect in the
school journal a lithograph of a plant called ‘Cook’s scurvy grass’. Fledgling botanist that I was then
this intrigued me. Aer all, the illustration of the plant so named looked more like a herb than a grass
to me. I wanted to know more about it of course but all I gleaned from the journal story was that Cook
instructed his crew to harvest lots of it, which he then fed, willingly or not, to them, so saving them
from scurvy.
Further reading later deduced that ‘Cook’s scurvy grass’ was not a grass at all but rather a kind of
cress in the genus Lepidium, L. oleraceum, allied to the cress plant Lepidium sativum which we used
to grow with mustard (Sinapsis arvensis) and then use as a sandwich lling. Cook it transpired used
the vernacular ‘scurvy grass’ because in his childhood he and his father went out foraging for ‘scurvy
grasses to supplement the family’s diet. While they
had a broad denition of ‘scurvy grass’ then, the
name was mostly applied, as it still is, to species
in the brassicaceous genus Cochlearia (Fig. 1). As
for me, I pretty much forgot all about scurvy grass
until 1981, when wandering through a book shop
in Wellington, I found a lovely book called ‘Rare
and Endangered Plants of New Zealand’ that had
just come out for sale. at book was written by
the late David Given (1943‒2005), and in it there
was a colour picture of ‘Cooks scurvy grass’. Given
(1981) noted that the plant was endangered with
extinction, repeated the tale about Cook using it
to cure scurvy, and then oered some reasons for
its demise. Like the school journal before, Given
repeated the story that Lepidium oleraceum was
once really common throughout New Zealand;
common enough that Cooks crew could collect
whole boat loads of it to make into scrumptious,
life-saving, salads.
My rst hands-on experience of Lepidium oleraceum came by accident in 1985 whilst engaged in a
second year University of Waikato Earth Science undergraduate paper that required eld work whilst
based at Port Waikato. One exercise involved mapping a coastal exposure at Ngatutura Point. Ngatutura
is located c.24 km south of Port Waikato, near the Kaawa River mouth on the rugged western Waikato
coastline. ere, whilst struggling up and down the cli faces, sketching, sampling rocks and taking
strike and dips I was amazed to nd some Cooks scurvy grass. at plant grew near the top of the
point in coastal turf, close to a towering near shore stack known as ‘Shag Rock’, on account of a spotted
shag (Phalacrocorax punctatus) colony that bred there. Binoculars soon conrmed that the plant I
found was probably derived from Shag Rock, where I could see many more growing in crevices below
and around the shag nests. I have since had the joy of seeing this plant and its close allies wild in an
array of places spanning from Dayrell Island in the Kermadecs to Otago Peninsula and the Chatham
Islands.
At the time Given (1981) wrote about it, Lepidium oleraceum was a name applied in a very broad sense.
Indeed, almost from the time it was rst described by Anders Sparrman (1780) the species was known
Figure 1. One of the European scurvy grasses, Cochlearia
ocinalis, seen here at Friesetraatweg, Groningen,
Netherlands. Species of Cochlearia were (and still are)
eaten by Europeans as a salad herb. Photo: A. Hospr.
5
to be ‘variable’ resulting in attempts to segregate that variation into taxonomic units. Pioneer botanist
omas Kirk (1828‒1898) for example, described two varieties Lepidium oleraceum var. acutidentatum
Kirk, and var. frondosum Kirk (Kirk 1899), and Albert ellung (1881–1928) recognised another,
var. serrulatum ell. (ellung 1906). However, by the time Harry Allan (1882–1957) assessed the
situation the application of these names had become confused (Allan 1961), in part because the
species was already in such serious decline that Given (1981) pessimistically attested that resolution of
these names based on what was le in the wild was likely now impossible. However, critical study of
Lepidium oleraceum throughout its range, supplemented with DNA based phylogenetic analyses and
patient study of the type specimens scattered around the world has resulted in a new interpretation
of the species (de Lange et al. 2013). at monograph redened Lepidium oleraceum, to encompass
those plants with glabrous (hairless) stems, persistent, toothed, stem leaves, glabrous pedicels, owers
with four stamens and by the acute silicles which lack a marginal wing (de Lange et al. 2013) (Fig. 2A
F). Plants matching these characters are known from the Kermadec Islands, North Island, northern
South Island and Chatham Islands. In the same treatment other plants that had been referred to L.
oleraceum were split into a further 10 species: L. aegrum Heenan et de Lange, L. castellanum de Lange
et Heenan, L. crassum Heenan et de Lange, L. juvencum Heenan et de Lange, L. limenophylax de
Lange, B.D.Rance et D.A.Norton, L. oblitum Houliston, Heenan et de Lange, L. oligodontum de Lange
et Heenan, L. panniforme de Lange et Heenan, L. rekohuense de Lange et Heenan and L. seditiosum de
Lange, Heenan et J.Rolfe (see de Lange et al. 2013).
Figure 2. Lepidium oleraceum in cultivation, Mt Albert, Auckland, showing diagnostic characters of this species: (A)
Foliage, (B) Flowering plant, (C) close up of foliage, owers and immature fruits, (D) owers showing the four stamens
that help distinguish L. oleraceum from other allied species in New Zealand, (E) mature and immature silicles – note the
lack of a marginal wing to the silicles, the acute silicle apex and lack of any notching, and (F) mature silicle and glabrous
pedicel. Photos: P.J. de Lange.
A
D
B
E
C
F
6
Taxonomy aside though, that research also uncovered a wealth of information and misinformation
about ‘Cook’s scurvy grass’.
e rst of these, that still needs further research, is the vexed question of whether Māori cultivated
Lepidium species. Long before the moniker ‘Cooks scurvy grass’ was ever coined iwi knew Lepidium
oleraceum and its allies by the name ‘nāu’. is name is potentially signicant, aer all it is not unique to
New Zealand; it is used for example by Cook Islanders for the supercially similar Lepidium bidentatum
Montin (Fig. 3A, B), and the name and variants of it appear throughout Polynesia for that species and
other allied lepidia. Discussions with the late Art Whistler (1944–2020) in 2010 helped conrm what
I had long suspected, that Lepidium bidentatum was not used solely as a vegetable by Cook Islanders
but rather that it was generically used throughout Polynesia, notably in Samoa and Tonga and the
Society Islands. It should therefore be no surprise that Lepidium oleraceum was bequeathed the same
name by those voyagers destined to become Māori. Now while I have never found convincing proof
that Māori deliberately grew it, comments about its abundance near Māori settlement made by the
Forster’s (Forster 1777; Hoare 1982) and observations by Joseph Banks, Daniel Solander who rst
collected it in New Zealand, and Captain James Cook suggest that iwi certainly ate it (Beaglehole
1962a, b; 1967, 1968) and that they probably did cultivate it. In a modern sense I have always felt that
the widespread usage by Māori of watercress (Nasturtium microphyllum and N. ocinale) as a salad
green and vegetable reects past mātauranga reecting the historical usage of nāu and perhaps also
Rorippa divaricata. is needs further study.
Figure 3. Lepidium bidentatum (in this case var. owaihiense) as seen on Maui in the Hawaiian Island group. is close
relative of Lepidium oleraceum was once wide ranging across the eastern Pacic where it was well known to many
Polynesian islanders as a vegetable and medicine. Photos: F. & K. Starr).
e second issue, which David Norton and I revisited in 1996, is whether folklore that Cook collected
‘boatloads’ of Lepidium oleraceum for use as a salad green to save his crew from scurvy is fact or
ction (de Lange & Norton 1996). If you remember, as a 10 year-old I learned that Cook instructed
his crew to collect scurvy grass, which they found in sucient quantities to collect in ‘boat loads’ to
sustain his hungry crew during their exploration of New Zealand. is story is widely accepted as
fact (see for example Moore & Irwin 1978), and has been used by such authorities as omas Kirk,
A B
7
omas Cheeseman, Lucy Moore and David Given as evidence that the formerly abundant Lepidium
oleraceum had suered a catastrophic decline that started soon aer Europeans began to settle the
country (Cheeseman 1914; Kirk 1899, Given 1981; Oliver 1925; Richards 1956; Moore & Irwin 1978;
Wilson 1982; Wilson & Given 1989).
at Lepidium oleraceum was once more abundant than it is now is evident from past accounts by early
voyagers, naturalists and resident botanists. However, critical assessment of the primary literature,
namely the journals of Captain Cook, Joseph Banks and the Forsters does not support the notion
that they were able to collect boat loads of Lepidium oleraceum (de Lange & Norton 1996). What they
did collect is a suite of edible coastal herbs, including Apium prostratum, Cardamine spp., Oxybasis
ambigua, Salicornia quinqueora, Te t r a g o n i a implexicoma, T. tetragonoides, and the brassicaceous
herbs Lepidium exicaule, L. oleraceum, Rorippa divaricata and R. palustre (de Lange & Norton 1996;
Norton et al. 1997; P.J. de Lange unpubl. data). e only place those early accounts noted Lepidium
oleraceum as abundant was Queen Charlotte Sound where it was considered common on a few islands,
notably Long Island (interestingly the Sounds remain a stronghold for Lepidium oleraceum). What
seems clear is that Cook instructed his scientic ocers and naturalists to look for edible plants, and
once these became known to the crew, they were widely collected as a dietary supplement.
Of these, the one plant the crew preferred to eat however, was Lepidium oleraceum. Consider the
comments of Anderson, a surgeon on Cooks third voyage, ‘Of other plants which were useful to us may
be reckond wild celery which grows plentifully almost in every cove, especially if the natives have ever
resided there before, and one which we us’d to call scurvy grass though entirely dierent from the plant we
gave the name to. It however is far preferable to it for common use and may be known by its jagged leaves
and small clusters of white owers on the top’ (Beaglehole 1967: 804).
Anderson’s remarks are not only an apt description of Lepidium oleraceum, this is also the rst time
that the vernacular scurvy grass is directly associated with that species. However, the rst usage of
‘Cook’s scurvy grass’ seems to have come much later, about the time of Kirk (1899). So the widespread
belief that Cook’s scurvy grass was once so common it could be collected by the boat load really has
no basis, rather it was one of a number of plants used by Cook and his crew and over time the broad
concept of ‘scurvy grass’ was narrowed to Lepidium oleraceum which eventually became the ‘C ook’s
scurvy grass’.
Lastly there is the matter of the decline of Lepidium ole raceum itself. What caused it? We do know that the
New Zealand archipelago was once dominated by seabirds (Fig. 4), and these birds played a critical role
in bringing nutrient from the sea to the land. is system, dubbed the ‘ornithocoprophilous ecosystem
(work that one out) by Bob (Robert) Orndu (1932–
2000) (Orndu 1965; Norton et al. 1997) received
scant attention by New Zealand ecologists until the
late 1980s, when it was ‘rediscovered’ (Ogle 1987). For
our early understanding of the system we owe much
to the pioneering work of Leonard Cockayne (1855–
1934) who described the vegetation patterns of many
predator free seabird islands but especially to Mary
Gillham (1921–2013) who had a particular interest in
these associations, and who in a series of landmark
papers (Gillham 1956, 1960a, b, 1961), some prepared
whilst on study leave from the United Kingdom in
New Zealand, documented the distinct vegetation
associations found on the so called ‘sea bird islands’
o our shoreline. Her work and that of Bob Orndu
noted a distinct correlation between particular plants
and seabird nesting sites. Some species they reasoned
Figure 4. Adult masked boobies (Sula dactylatra
tasmani) roosting on North Chanter, Herald Islets,
northern Kermadec Islands group. ese birds and
others that nest and roost on this island are part of an
intact and functional ornithocoprophilous ecosystem,
that was once widespread throughout the adjacent
New Zealand Archipelago. Photo: P.J. de Lange.
8
were utterly dependent on sea birds to maintain their habitat and perhaps for their growth and
persistence. One of those plants was Lepidium oleraceum sens. lat.
Norton et al. (1997) reasoned that, following the colonisation of the New Zealand archipelago by
humanity, the subsequent spread of introduced mammalian predators resulted in range contractions
and local extirpations of the vegetation associated with seabirds. ey concluded that this contraction
meant that plants such as Lepidium olerace um were already in decline by the time they were rediscovered
and formally described by European botanists. However, they also reasoned that in those places where
the ornithocoprophilous ecosystem remained intact the vegetation associated with that system would
persist. What they noted was that in such places while this was true there continued to be local
extirpation of key species such as Lepidium oleraceum sens. lat. So seabird decline whilst a factor was
not the sole reason for the decline.
Kirk (1891) and Cheeseman (1914, 1925) attributed declines to direct browse pressure by sheep (Ovis
aries) and cattle (Bos taurus taurus), Norton et al. (1997) suggested that rats (Rattus spp.) also have
impacted the species through the direct browse of plants (indirectly rats are a key factor in that they
contributed to the decline of seabirds). It is also evident that possum (Trichosurus vulpecula) are now
a factor impacting members of the Lepidium oleraceum group throughout accessible sites in the North
and South Islands and on Rekohu (Chatham Island). Esler (1975) and Given (1981) amongst others
attributed an acceleration of decline to the accidental
introduction of cabbage white butteries (Pieris
rapae) to New Zealand, it is thought, over the summer
of 1929–1930 (it was ocially recognised here in 1930
from specimens collected from Napier). As anyone
who has grown Lepidium oleraceum will appreciate,
cabbage white butteries are a real pest (Fig. 5.) but
there are others. For example, Ogle (1987) noted the
impact of cabbage aphid (Brevicoryne brassicae) and
diamond backed moth (Plutella maculipennis) as well
as a host of other introduced invertebrates. It cannot
be doubted that these introductions have contributed
and continue to contribute to further losses.
e conclusion reached by Norton et al. (1997) was that to retain Lepidium oleraceum populations
it is critical to retain seabird breeding grounds. ey reasoned, in line with the thinking of others
such as Mary Gillham, that seabirds and seals contributed both nutrients and disturbance, so keeping
sites open. Recently Dale et al. (2017) explored whether seabirds were essential to facilitate seed
germination in Lepidium, discovering that seed germination was not promoted by seabird guano
but that the seeds are probably dispersed by seabirds. ey discovered that wetted seed releases a
mucilage which enables seed to adhere to surfaces for over 24 months. at discovery may explain
how Lepidium oleraceum in particular has such a wide geographic spread. It also shows that the overly
simplistic assumptions of the importance of the nutrients le by seabirds and seals in promoting
seed germination, growth and population resilience need further research. Nevertheless, as anyone
who has tried growing Lepidium oleraceum will appreciate, plants ourish with regular applications
of Nitrogen, Phosphorus fertilisers, and some gardeners use such fertilisers as a way to control the
damaging eects of ‘white rust’ (Albugo) (Fig. 6A, B), noting that well fed plants seem to ‘out-grow’
the disease. e same logic has been employed by the Department of Conservation with managing
Lepidium banksii and L. rekohuense, whereby plants are routinely ‘over fertilised’ to help them thrive
in the wild (P.J. de Lange unpubl. data).
So what is the deal with Albugo? at organism has over the last 20 years become a major concern
when managing Lepidium populations (Norton & de Lange 1999). Albugo is actually not a rust at all
rather it is an oomycete, so more closely related to Phytophthora for example, nevertheless it is widely
Figure 5. Cabbage white buttery caterpillar (Pieris
rapae) on Lepidium oleraceum. Photo C.C. Ogle.
9
A
B
Figure 6. Albugo candida infecting (A) shepherd’s purse (Capsella bursa-pastoris) (Te One, Rekohu / Wharekauri / Chatham
Island) and (B) rocket (Eruca sativa subsp. vesicaria) (Mt Albert, Auckland). Photos: P.J. de Lange.
known as ‘white rust’ on account of the white pustules it produces during its reproductive stage. Albugo
is now widely acknowledged as a serious threat to New Zealand indigenous Brassicaceae, and, in
particular Lepidium (Norton et al. 1997; de Lange et al. 2013). Albugo is most evident when the white
pustules appear but it has been discovered that it commonly occurs as asymptomatic infections with
one study noting it present in a range of apparently healthy Lepidium oleraceum plants spanning that
species range (Armstrong 2007). Albugo pustules may appear all over an aicted plant, however, they
are most commonly seen on young foliage and inorescences (including ower buds, owers) and
developing fruits (Fig. 7), thus reducing the host plants ability to thrive and reproduce. Death from
severe Albugo infection has been reported in wild populations of Lepidium banksii, L. oligodontum and
L. panniforme (de Lange et al. 2013). Despite a range of treatments, none used to date can truly be said
to be eective, and some, such as the use of the fungicide Ridomil Gold® that is used in the treatment
of some oomycete diseases, while slowing the visible
pustule stages of Albugo are not in the long-term
environmentally suitable for use in natural habitats.
Worryingly, reports of Albugo attacking New Zealand
indigenous Brassicaceae have increased in the last
three years, with some seriously threatened species
such as the South Island salt pan endemic Lepidium
kirkii Petrie, and dioecious L. sisymbrioides Hook.f.
and L. solandri Kirk now possibly in terminal decline
because of this disease. Until recently the Albugo
aicting our indigenous Lepidium was assumed to be
A. candida (Pers. ex J.F.Gmel.) Kuntze. is follows on
from the only comprehensive study of the genus in
New Zealand undertaken, that by Baker (1955). In
that paper she treated what we now call A. candida as
A. cruciferarum S.F.Gray, and considered it introduced
on the basis that it was rst recorded from New
Zealand by William Colenso in 1886. To counter this
view though is the fact that few people were at that
time actively collecting these sorts of organisms, so it
may have been here longer, possibly naturally so.
ere have even been some doubts raised as to
Figure 7. Lepidium oligodo ntum plant severely infected
by Albugo (Moriori Creek, southern tablelands,
Rekohu / Wharekauri / Chatham Island). Photo: P.J.
de Lange.
10
whether the Albugo reported from New Zealand is actually A. candida; judging by its presence
throughout the range of New Zealand’s indigenous lepidia, and the life cycle of some species such as
L. oligodontum that seem to ‘t around’ the impact of this disease (de Lange et al. 2013). As such a
revisit into the taxonomy of Albugo here has long been desired.
Recently, Dr Jerry Cooper of Landcare Research has
been investigating those infections attributed to Albugo
candida, notably in the South Island inland dioecious
lepidia, L. sisymbrioides and L. solandri. Using DNA,
Cooper has discovered that the Albugo infecting
these two species is not A. candida but A. lepidii
A.N.S.Rao (Fig. 8), and as a result of that discovery
Jerry expanded his research to cover Chatham
Islands lepidia, including L. oleraceum, nding the
same Albugo species was involved (see for example,
https://inaturalist.nz/observations/24541077). Jerry
also found that Albugo candida is in New Zealand
but that it attacks other exotic Brassicaceae. It would
seem that Albugo lepidii is also introduced. Hopefully
this knowledge may enable better management of the
disease in the wild.
So returning to the original question of what caused / is causing the decline of Lepidium oleraceum in
New Zealand? e answer is linked to the historical collapse of the ornithocoprophilous ecosystem,
resulting in population fragmentation and loss of functionality, followed by a steady increase of
pressures on remnant populations from introduced predators, weeds and diseases. None of these are
easily resolved but the good news is people are trying and in the case of some species, such as Lepidium
banksii and L. rekohuense, they are so far staving o extinction.
Acknowledgements
When I started writing this article I received the tragic news that the ongoing COVID-19 outbreak
had caused the death of Art Whistler (1944‒2020) whom I had assisted with reviews of his threatened
plant surveys of Samoa, and in turn had learned so much of the ethnobotany of the Polynesian
peoples (Art’s life-long research passion). Art was convinced that Polynesians used and probably grew
Lepidium bidentatum, and fascinated about the etymological connections between the names nāu,
n’au and k’ao used for coastal lepidia in the eastern Pacic. I do hope people reading this are stimulated
to make a study of the subject. As for me, I have been fascinated by tales of Cook’s scurvy grass since
I was 10, and over the many years since then I have had the pleasure of working with a ra of people
on this fascinating plant and its allies. In particular, I would like to acknowledge the late David Given
and Bob Orndu for sharing their wisdom and interest in the plant and the ecosystem it inhabits. I
thank also David Norton of the School of Forestry, University of Canterbury, with whom I worked in
the 1990s, especially on New Zealand Lepidium and Jerry Cooper for taking a fresh interest in Albugo
and sorting out a little of the mess that awaits anyone dealing with that dicult genus. anks also
to Peter Heenan, Gary Houliston and Jeremy Rolfe for their help with the taxonomic revision of the
complex. While it would seem we are a long way o halting the decline of these amazing plants, there
is still hope this can be achieved.
References
Armstrong, T. 2007: Molecular detection and pathology of the oomycete Albugo candida (white rust) in threatened coastal
cresses. DOC Research and Development Series 274. Department of Conservation, Wellington.
Baker, S.D. 1955: e genus Albugo in New Zealand. Transactions of the Royal Society of New Zealand 82: 987‒993.
Beaglehole, J.C. 1962a: The Endeavour journal of Joseph Banks 1768-1771. Volume I. Trustees of the Public Library of New
South Wales, Sydney.
Figure 8. Albugo lepidii pustules on the rosette leaf of
Lepidium oligodontum (Point Somes, Waitangi West,
Rekohu / Wharekauri / Chatham Island). Photo: P.J.
de Lange.
11
Beaglehole, J.C. 1962b: e Endeavour journal of Joseph Banks 1768-1771. Volume II. Trustees of the Public Library of New
South Wales, Sydney.
Beaglehole, J.C. 1967: e journals of Captain James Cook on his voyages of discovery. III. e voyage of the Resolution and
Discovery 1776-1780. Parts 1 and 2. Hakluyt Society and Cambridge University Press, Cambridge.
Beaglehole, J.C. 1968: e journals of Captain James Cook on his voyages of discovery. I. e voyage of the Endeavour 1768-
1771. Hakluyt Society and Cambridge University Press, Cambridge.
Cheeseman, T.F. 1914: Illustrations of the New Zealand ora. Volume 1. Government Printer, Wellington.
Cheeseman, T.F. 1925: Manual of the New Zealand Flora. Second Edition. Government Printer, Wellington.
Dale, E.; de Lange, P.; Burns, B. 2017: Seed dispersal but not seed germination facilitated by seabirds: seed ecology of
Cook’s scurvy grass. New Zealand Journal of Ecology 41: 226‒233.
de Lange, P.J.; Norton, D.A. 1996: To what New Zealand plant does the vernacular “scurvy grass” refer? New Zealand
Journal of Botany 34: 417‒420.
de Lange, P.J.; Heenan, P.B.; Houliston, G.J.; Rolfe, J.R.; Mitchell, A.D. 2013: New Lepidium (Brassicaceae) from New
Zealand. PhytoKeys 24: 1‒147.
Esler, A.E. 1975: Vegetation of the sand country bordering the Waitakere Range, Auckland: Piha Beach. Proceedings of the
New Zealand Ecology Society 22: 52‒56.
Forster, G. 1777: Voyage round the world in His Britannic Majesties Sloop Resolution, commanded by Capt. James Cook,
during the years 1772, 3, 4 and 5. Elmsly and Robinson, London.
Gillham, M.E. 1956: Ecology of Pembrokeshire Islands. V. Manuring by the colonial seabirds and mammals with a note on
seed distribution by hulls. Journal of Ecology 44: 429‒454.
Gillham, M.E. 1960a: Plant communities of the Mokohinau Islands. Transactions of the Royal Society of New Zealand 88:
79‒98.
Gillham, M.E. 1960b: Vegetation of New Zealand Shag colonies. Transactions of the Royal Society of New Zealand 88:
363‒380.
Gillham, M.E. 1961: Alteration of the breeding habitat by sea-birds and seals in western Australia. Journal of Ecology 49:
289‒300.
Given, D.R. 1981: Rare and endangered plants of New Zealand. Reed, Wellington.
Hoare, M.E. (ed.) 1982: e ‘Resolution’ Journal of Johann Reinhold Forster 1772–1775. Vol. I–IV. Hakluyt Society, London.
Kirk, T. 1891: Descriptions of new plants from the vicinity of Port Nicholson. Transactions of the New Zealand Institute
24: 423‒425.
Kirk, T. 1899: e Students’ Flora of New Zealand and the Outlying Islands. Wellington, N.Z., Government Printer.
Moore, L.B.; Irwin, J.B. 1978: e Oxford book of New Zealand plants. Oxford University Press, New Zealand.
Norton, D.A.; de Lange, P.J. 1999: Coastal cresses (Nāu) recovery plan. Wellington, Department of Conservation.
Norton, D.A.; de Lange, P.J.; Given, D.R.; Garnock-Jones, P.J. 1997: e role of sea birds and seals in the survival of coastal
plants: lessons from New Zealand Lepidium (Brassicaceae). Biodiversity and Conservation 6: 765‒785.
Ogle, C.C. 1987: e retreat of Cook’s scurvy grass. Forest & Bird 18: 26.
Oliver, W.R.B. 1925: Vegetation of Poor Knights Islands. New Zealand Journal of Science and Technology 7: 376-384.
Orndu, R. 1960: An interpretation of the Senecio lautus complex in New Zealand. Transactions of the Royal Society of New
Zealand 88: 63‒77.
Orndu, R. 1965: Ornithocoprophilous endemisim in Pacic Basin angiosperms. Ecology 46: 864‒807.
Richards, E.C. 1956: Our New Zealand trees and owers. 3rd ed. Simpson & Williams, Christchurch.
Sparmann, A. 1780: Tres novae plantae, descriptae. Nova Acta Regiae Societatis Scientiarum Upsaliensis 3: 190-195.
ellung, A. 1906: Die Gattung Lepidium (L.) R. Br. Eine Monographische Studie. Basel.
Wilson, H.D. 1982: Stewart Island plants: eld guide. Field Guide Productions, Christchurch.
Wilson, C.M.; Given, D.R. 1989: reatened plants of New Zealand. DSIR, Wellington.
Funds available for possum control
e New Zealand Plant Conservation Network has the sum of $1,500.00 available for a possum control
project within New Zealand. is has arisen from a self-imposed Possum Tax levy on members of
the Australasian Systematic Botany Society (ASBS) during their attendance at the 2019 Joint ASBS-
NZPCN Conference in Wellington. e NZPCN has matched the amount raised by their Australian
counterparts and is now making these funds available for a suitable project within New Zealand.
e only criteria for applications for this funding are that the project must entail possum control and it
should ideally involve a threatened native plant species. Applications are now invited and should be sent
via email to info@nzpcn.org.nz. Final deadline for submission of applications is Tuesday 30 June 2020.
e successful application will be published in an upcoming issue of Trilepidea and a post-project
story will be published at a later date.
12
What value do you put on biodiversity (in a pandemic)?
e NZ Native Forest Restoration Trust
Even as the NZ Native Forest Restoration Trust were negotiating the purchase of Otatara sand dune
totara forest mentioned in last months Trilepidea, members of the Rotorua Botanical Society were
suggesting to Bay of Plenty Regional Council sta that they should ask the Trust for help to save a 14
hectare sand dune kanuka forest at ornton Beach west of Whakatane. Not just any patch of kānuka,
but the only 14 hectare patch in private ownership of Kunzea toelkenii. is species, described in 2014,
does not grow anywhere beyond the ornton beach front and a couple of nearby islands.
Current Conservation Status—2018: reatened – Nationally Critical
For detail on Kunzea toelkenii refer to http://www.nzpcn.org.nz/ora_details.aspx?ID=7642 or
de Lange, P.J. 2014: A revision of the New Zealand Kunzea ericoides (Myrtaceae) complex.
Quote from de Lange: “erefore, formal taxonomic
recognition is accorded here to any Kunzea entity
which demonstrates consistent morphological,
cytological, molecular and ecological partitioning
irrespective of whether it can or does hybridise,……
Ecologically, Kunzea toelkenii is further
distinguished as the only member of the K. ericoides
complex truly endemic to sand dune systems.
While the Trust has NOT made a nal decision to
purchase the ornton beach property, we do see
the desperate need for it to be protected. To assist us
it would be helpful to have an indication of potential
support if we decide to buy. We hope you too can
see the future with the weird and wonderful Kunzea
toelkenii lining the beachfront at ornton.
We are asking the following questions:
Would you be in a position to make a donation?
If so what gure do you consider possible?
Alternatively, could you advance a loan to the Trust at very low interest (or zero).
We envisage a 2 to 5 year term. How much could you lend us, and for how long?
Alternatively, if you would like a beach front section in the Bay of Plenty, do contact us
e real estate advertisement is at https://nz.raywhite.com/whakatane-district/thornton/2236093/
You can contact us at admin@nznfrt.org.nz or view our website at www.nfrt.org.nz
If you would like to communicate with a Trustee, please email Geo Davidson at geo.bev.davidson@
gmail.com or phone him on 09 813 0229 or 021 764 967.
e contorted form of a typical ornton beach Kunzea
toelkenii. Starting life as prostrate shrubs, they form
dense thickets of foliage, developing numerous trunks
and opening into sprawling adults aer 30 years.
13
UPCOMING EVENTS
If you have events or news that you would like publicised via this newsletter please email the Network
(events@nzpcn.org.nz).
Please Note: It is strongly recommended that you contact your local Botanical Society to conrm
whether the advertised meetings and eld trips are proceeding as originally planned or whether
there are meetings or eld trips happening that are not advertised. e New Zealand Plant
Conservation Network accepts no responsibility for changes to the published details.
Auckland Botanical Society
Meetings and Field Trips: Cancelled until further notice.
Rotorua Botanical Society
Field Trip: Saturday 6 June to Matata sand dunes and coastal
lagoon. Meet: 8.00am at the Rotorua carpark or 9.00am at the
Matata campground carpark. Grade: Easy.
Leader: Sarah Beadel, email sarah.
beadel@wildlands.co.nz,
ph. 021 924 476.
Meeting: Monday 15 June at 6.00pm – AGM, followed by guest
speaker. Wine, juice, cheese and nibbles will be provided.
Venue: To be advised.
Wellington Botanical Society
Field Trips: Saturday 6 June. Postponed to 3 October.
Meeting: Monday 22 June (by Zoom only at this stage) – Speaker
Mark Alpine and others from the Greater Wellington Regional
Council. Topic: whats happening in weed bio-control in the
Wellington region.
Venue (if meeting in person):
Lecture Theatre M101, ground
oor Murphy Building, west side of
Kelburn Parade.
Nelson Botanical Society
Field Trips: Cancelled until further notice.
Canterbury Botanical Society
Meetings: By Zoom or similar only at this stage.
Field Trips: Cancelled until further notice.
Botanical Society of Otago
Field Trips: Cancelled until further notice.
Meeting: Wednesday 10 June at 5.20pm – Speaker Dr Allison
Knight. Topic: Sexy Lichens.
Venue: Room 215, 2nd Floor,
Zoology Benham Building, 346
Great King Street.
ResearchGate has not been able to resolve any citations for this publication.
Article
Full-text available
The rediscovery of Lepidium oleraceum (Cook's scurvy grass) is reported for Mana Island, Wellington. The national decline of Cook's scurvy grass is summarised, and possible reasons for the decline are suggested, including the loss of high fertility sites through the actions of mammalian predators on mainland seabird colonies.
Article
Full-text available
The term “scurvy grass” is used widely in New Zealand as a vernacular for the formerly widespread brassicaceous herb Lepidium oleraceum. We show that historical usage of this vernacular was not necessarily confined to this species or genus, thereby illustrating the need for caution in using historical accounts to help determine past abundance, ecology, and distribution.
Article
Captain James Cook’s first two voyages of exploration, in 1768-71 and 1772-75, had drawn the modern map of the South Pacific Ocean and had opened the door on the discovery of Antarctica. These expeditions were the subject of Volumes I and II of Dr J.C. Beaglehole’s edition of Cook’s Journals. The third voyage, on which Cook sailed in 1776, was directed to the Northern Hemisphere. Its objective was the discovery of ‘a Northern Passage by sea from the Pacific to the Atlantic Ocean’ - the North-west Passage, sought since the 16th century, which would have transformed the pattern of world trade. The search was to take Cook into high latitudes where, as in the Antarctic, his skill in ice navigation was tested. Sailing north from Tahiti in 1778, cook made the first recorded discovery of the Hawaiian Islands. On March 7 he sighted the Oregon coast in 44° N. The remarkable voyage which he made northward along the Canadian and Alaskan coasts and through Bering Strait to his farthest north in 70° nearly disproved the existence of a navigable passage towards the Atlantic and produced charts of impressive accuracy. Returning to Hawaii to refit, Cook met his death in a clash with the natives as tragic as it seems unnecessary. Dr Beaglehole discusses, with sympathy and insight, the tensions which led Cook, by then a tired man, into miscalculations alien to his own nature and habits. The volume and vitality of the records, both textual and graphic, for this voyage surpass those even for Cook’s second voyage. Dr Beaglehole prints the full text of Cook’s own holograph journals, followed by those of Captains Clerke and King for the course of the voyage after Cook’s death. The documentation is completed, as in the previous volumes, by appendixes of documents and correspondence and by reproductions of original drawings and paintings mainly by John Webber, the artist of the expedition. In Dr Beaglehole’s words, ‘no one can study attentively the records of Cook’s third, and last, voyage, without being convinced that it was of the same order of greatness as its two predecessors’. Even if it failed in the object set out in Cook’s instructions, it made an extraordinary contribution to geographical knowledge; and it embraces both intellectual and psychological drama. In presenting the materials for understanding this voyage, Dr Beaglehole shows no less mastery and perceptiveness than in his earlier volumes. This is a facsimile reprint of the edition published in 1967. For the print-on-demand edition, the illustrations originally in colour are reproduced in black-and-white, the fold-outs divided to fit on separate pages, and teh volume itself split into two parts.
Article
Writing of inland birds in America, Beecher (1942,) states `The animal population can be no more stable than the plant community in which it occurs'. This statement has even closer significance when applied to islands of south-west Australia, where the greater numbers of larger birds nesting in closer proximity are themselves largely responsible for the instability of the plant communities in which they live. The colonial habit of the majority of sea birds leads to heavy local guano deposition and trampling and the plant community is radically changed or destroyed altogether. During the initial phases this may be of advantage to the birds - in the later phases it is almost invariably to their detriment. The nesting and roosting of cormorants in bushes results in the death of the bushes and necessitates frequent changes of site. Expanding populations of gulls spreading into scrub also causes death of the bushes, but the open community of herbs which replaces them provides a more suitable habitat for the gulls. Subsequent destruction of all plant life renders the habitat unsuitable. Burrowing birds (penguins, petrels and shearwaters) are less inimical to vegetation than are surface nesters and are able to remain faithful to the ancestral breeding grounds as others are not. Destruction of sheltering vegetation may occur, however, and erosion is initiated from burrow entrances. Widespread collapse of burrows on shallow soils or mobile sands necessitates a general exodus to another site. By stimulating low-growing `shelter plants' beneath open-based shrubs, penguins create a temporary improvement in their habitat, whilst cormorants, in destroying the habitat for themselves, make it more suitable for birds of the open. Thus one species of bird mingles with or follows another on the chosen sites and periodic movements between a group of potential sites affords opportunity for the vegetation to recover during the birds' absence. Plant cycles involving degeneration of climatic climax communities to the point where all plants are annihilated and subsequent regeneration to altered plagioclimax or sub-climax communities are discussed. The general trend of degeneration is from sclerophyllous shrubs through hairy, silver-leaved shrubs and succulent-leaved shrubs to succulent, perennial creepers and finally to annuals, many of which are introduced. After the end point of bare soil has been reached, regeneration follows a similar course in reverse, but recolonization by birds usually occurs before the original climax has been attained. Similar trends are seen in seal nursery vegetation.
Article
(1) Deposition of guano is one of the most influential habitat factors in the bird colonies, selecting towards a similar type of flora in widely divergent areas. (2) Rabbit pellets are of little importance to the soil nutrient content except in non-organic cliff soils newly exposed by erosion. The dung of Soay sheep is most influential in the cliff sheltering grounds. (3) Deposition of seabird manure in summer is very concentrated locally and greatly enriches the soil, the material added being brought chiefly from the sea or the adjacent mainland. (4) All vegetation is eliminated where deposition of guano is most intense as in the Grassholm gannetry. Where slightly less intense, as in the Stellarietum of the Middleholm gull roost, only a few specialized nitrophiles can exist. (5) In shearwater colonies a high proportion of the defaecation takes place inside the burrows, diffusely throughout their ramifications. (6) In puffin colonies deposition occurs in three main areas, on the communal cliff edge `standing grounds', at the burrow entrances and in special defaecation chambers within the burrows. (7) Defaecation by razorbills may be directly on to mats of Agrostis stolonifera, which suffer little harm as a result. (8) Areas most affected in the gull colonies are the feeding, preening and observation areas, defaecation in the immediate vicinity of the nest being often less. (9) Guano contains nitrogen, phosphate, potash and lime and is stimulatory to most plants when in moderate amounts. Feathers and food remains also add to the soil nutrient content. (10) The amount of nitrate in the soil is closely dependent on the deposition of manure and ranges from the equivalent of 0-2 lb./acre in areas unfrequented by the vertebrate fauna to over 100 lb./acre where manuring is concentrated. Mammals increase the soil nitrate content 20-40 fold, birds 100 fold, amounts in the nesting colonies having decreased by about 50 per cent six weeks after the birds have left in autumn. The C:N ratio is not usually low enough to suppress flowering. (11) Soil phosphate content is closely related to the amount of guano present and ranges from 0.02 per cent in areas remote from the birds to 0.7 per cent where defaecation is heavy. Guano samples contained up to 12.84 per cent, rabbit dung 0.5 per cent. (12) Exchangeable calcium and carbonate of the soil are little affected by guano, being more closely related to the amount of organic matter present. (13) Both guano and salt make the soil reaction more alkaline where they occur separately but there appears to be interaction between the two in coastal soils. In soils affected by blown salt spray guano has no effect on soil pH; in soils subjected to inundation by salt water it causes increased acidity. Downward penetration of the alkaline consistuents of guano is greatest in non-organic soils poor in mineral nutrients, less in non-organic soils to which fertilizers had been added, least in retentive organic soils. (14) Organic matter of avian origin has a low water-retaining capacity when compared with humus from mammalian dung or from the direct decomposition of plant material. (15) The stimulatory effect of guano on vegetation is usually seen only on inaccessible slopes below the breeding colonies and after the birds have left for the winter. Elsewhere it is counteracted by the suppressive effects of trampling, burrowing, rabbit grazing and `scorching' by the guano itself. (16) Under the latter conditions Plantago coronopus is the most characteristic nitrophile. In more favourable environments Silene maritima and Rumex acetosa are typical, the latter being particularly robust over the parts of the puffin burrows in which defaecation occurs. The most favourable habitats show rank growths of Umbilicus, Cochlearia, Atriplex, Beta, Rumex and Matricaria, the burrow entrances of Stellaria and Poa. (17) Deposition of guano in inland areas causes some of the usual mesophytes to be replaced by halophytic nitrophiles more typical of the cliffs. Plants of inland bird colonies are less resistant to droughts during the nesting season than are those of coastal bird colonies. (18) Degeneration of Callunetum to Agrostidetum may be partly due to occupation by gulls. Armerietum previously occupied by gulls has changed through a Senecionetum to a Holcus-Rumex community. (19) Areas too heavily fouled for growth of angiosperms may support terrestrial algae (principally Prasiola crispa) or lichens (principally Xanthoria and Lecanora). Larger fungi and most bryophytes are intolerant of guano, Ceratodon, Eurhvnchium and a few other mosses are stimulated by it. (20) Gulls feeding on the mainland are important agents in the transport of seeds to the islands. Viable seeds are frequently found in their pellets and colonies of cereals and arable weeds are common in the cliff feeding grounds.
Article
Captain James Cook, RN, FRS, has been rightly called ̀the greatest explorer of his age, the greatest maritime explorer of his country in any agè. On the three expeditions which he led to the Pacific between 1768 and his death at Hawaii in 1779, his ships thrice circled the globe; he drew the modern map of the Pacific, and he was the first European seaman to circumnavigate New Zealand, to discover the east coast of Australia, to cross the Antarctic Circle, to chart the north–west coasts of America. From his ships the scurvy that had made a hell of long sea voyages was banished, and on his second voyage of over three years he lost not one man from this disease. The three voyages proclaim his greatness alike as a seaman and navigator, an explorer, a practical scientist, and a leader of men. They were worthily chronicled in his own Journals and charts. It is a reproach to scholarship that Cook's own record of his voyages has never till now been faithfully reproduced from the manuscripts written in his hand. In this edition, prepared for the Hakluyt Society, the text has been printed from surviving holograph Journals by Cook, under the editorship of Dr J.C. Beaglehole, of Victoria University College, Wellington, who has for many years dedicated himself to the study of Cook and his career in exploration. The work is in four volumes (originally with a separate Portfolio containing reproductions of original charts and views drawn on the three voyages; these were subsequently republished separately by the Hakluyt Society). This first volume deals with the voyage of the Endeavour, 1768-1771. Prefixed to it is a General Introduction on the exploration of the Pacific before Cook. The illustrations reproduce original drawings and paintings (many now published for the first time), portraits, documents and maps. This is a facsimile of the edition first published in 1955, along with the Addenda and Corrigenda published in 1968. For the print-on-demand edition, the illustrations originally in colour are reproduced in black-and-white, the fold-outs divided to fit on separate pages, and the volume split into two parts.
Article
The residual effects of fire on snow tussock (Chionochloa rigida (Raoul) Zotov) were examined in five areas of tussock grassland at between 500 m and 650 m altitude on Flagstaff, Dunedin. Three sites at different altitudes had been burnt in the spring of 1976, one the previous autumn, and one had not been burnt for at least 25 years.The spring-burnt sites generally had lower canopy cover, tiller density and above-ground biomass than the unburnt site. The two upper spring-burnt sites had significantly lower tiller weight and total leaf length than the other three sites, however the ratio of green to the total leaf length was highest in the uppermost spring-burnt site.The autumn-burnt site differed significantly from the unburnt only in having a greater sheath:total leaf length.The previous belief that spring fires are less damaging to C. rigida tussocks than autumn fires requires further investigation. It is suggested that future studies of the response of C. rigida to fire should include detailed measurements of both tiller and tussock characteristics.
Article
Thesis (M.S.)--University of Washington. Bibliography: L. [47]-51.