Fast-forward to the present day, and much of our current scientific
knowledge of global plant and fungal diversity comes from specimens
hosted by the world’s herbaria and fungaria, of which there are more
than 3,000. But despite this wealth of knowledge and collections, one
might be surprised to learn that, to date, we have not been able to
answer one of the most fundamental questions in plant and fungal
diversity with confidence – namely, how many species are there globally
and in different parts of the world?
The consequences of our insufficient knowledge on biodiversity and
distribution are manifold. Scientists may have drawn biased – or
possibly even incorrect – conclusions on the patterns and underlying
drivers of diversity. Beyond the impacts of knowledge gaps and
inaccuracies on efforts to answer fundamental scientific questions,
there are serious implications for conservation given that several
targets in the Kunming–Montreal Global Biodiversity Framework, such as
those related to protecting and restoring biodiverse habitats, rely on
having robust biodiversity data.
Around the world, myriad Lifeforms have evolved to depend On each
other in complex ways. This biodiversity, at scales from Single genes to
entire ecosystems, Is essential for our existence.
Plants, in particular, provide us with food, materials, medicines and
more. They regulate important planetary cycles that provide us with the
air we breathe and water we drink, and contribute to our overall
well-being.
If we are to safeguard life on Earth, we must end the current
extinction crisis in which plant species are dying out at least 500
times faster than before humans existed.
But with limited time and resources, we need to know how best to
conserve biodiversity to keep ecosystems diverse and functioning, while
preserving species with the greatest potential for use by future human
population.
Researchers measure biodiversity in different ways, including by
considering the distinctiveness of species resulting from their
evolutionary history.
Diverse evolutionary lineages underpin an ecosystem’s resilience to
environmental change.
Traditionally, conservation has focused on species richness and
endemism. However, phylogenetic diversity, which takes account of
evolutionary history, is a more effective measure of capturing diversity
and ensuring ecosystems remain resilient.
The maps show that phylogenetic diversity is more evenly distributed
across the globe, so current conservation priorities may need to be
rethought to ensure critical biodiversity is not lost.
32 plant data darkspots have been identified worldwide. Fourteen are
within tropical Asia, nine within South America, six in temperate Asia,
two in Africa, and one in North America.
They are the dark matter of botany – plant species that are yet to be
scientifically named, described and mapped but which are estimated to
make up 15% of the world’s flora. As well as being part of the
global
With 77% of undescribed species predicted to be threatened with
extinction (see Chapter 9), the race is on to find and conserve
them.
Many species that are unknown to science are, in fact, well known to
indigenous communities.
Iran is one of six plant diversity darkspots located within temperate
Asia.
The largest knowledge gaps on plant diversity and distribution occur
in Colombia.
New Guinea comes second in terms of knowledge gaps and is also the
only country not to overlap with the current global Biodiversity
Hotspots.
Madagascar and cape provinces have the greatest combined data gaps
for Africa.
Overall, the work indicated that if recent trends in scientifically
describing and mapping new plant species continue, current botanical
collection may be insufficient to completely document the geographical
distribution of all vascular plants in the near future.
And while the current Biodiversity Hotspot classification is regarded
as a useful framework to guide biodiversity scientists and
conservationists, the new research findings show that the Hotspots alone
are not enough to inform collection priorities. Rather, in parallel with
the findings outlined in Chapter 6, they indicate that considering plant
diversity darkspots in conjunction with Hotspots would be a better
approach going forward.
Citation
Antonelli, A., Fry, C., Smith, R.J., Eden, J., Govaerts, R.H.A.,
Kersey, P., Nic Lughadha, E., Onstein, R.E., Simmonds, M.S.J., Zizka,
A., Ackerman, J.D., Adams, V.M., Ainsworth, A.M., Albouy, C., Allen,
A.P., Allen, S.P., Allio, R., Auld. T.D., Bachman, S.P., Baker, W.J.,
Barrett, R.L., Beaulieu, J.M., Bellot, S., Black, N., Boehnisch, G.,
Bogarín, D., Boyko, J.D., Brown, M.J.M., Budden, A., Bureš, P., Butt,
N., Cabral, A., Cai, L., Aguilar-Cano, J.A., Chang, Y., Charitonidou,
M., Chau, J.H., Cheek, M., Chomicki, G., Coiro, M., Colli-Silva, M.,
Condamine, F.L., Crayn, D.M., Cribb, P., Cuervo-Robayo, A.P., Dahlberg,
A., Deklerck, V., Denelle, P., Dhanjal-Adams, K.L., Druzhinina, I.,
Eiserhardt, W.L., Elliott, T.L., Enquist, B.J., Escudero, M.,
Espinosa-Ruiz, S., Fay, M.F., Fernández, M., Flanagan, N.S., Forest, F.,
Fowler, R.M., Freiberg, M., Gallagher, R.V., Gaya, E., Gehrke, B.,
Gelwick, K., Grace, O.M., Granados Mendoza, C., Grenié, M., Groom, Q.J.,
Hackel, J., Hagen, E.R., Hágsater, E., Halley, J.M., Hu, A.-Q,,
Jaramillo, C., Kattge, J., Keith, D.A., Kirk, P., Kissling, W.D., Knapp,
S., Kreft, H., Kuhnhäuser, B.G., Larridon, I., Leão, T.C.C., Leitch,
I.J., Liimatainen, K., Lim, J.Y., Lucas, E., Lücking, R., Luján, M.,
Luo, A., Magallón, S., Maitner, B., Márquez-Corro, J.I., Martín-Bravo,
S., Martins-Cunha, K., Mashau, A.C., Mauad, A.V., Maurin, O., Medina
Lemos, R., Merow, C., Michelangeli, F.A., Mifsud, J.C.O., Mikryukov, V.,
Moat, J., Monro, A.K., Muasya, A.M., Mueller, G.M., Muellner-Riehl,
A.N., Nargar, K., Negrão, R., Nicolson, N., Niskanen, T., Oliveira
Andrino, C., Olmstead, R.G., Ondo, I., Oses, L., Parra-Sánchez, E.,
Paton, A.J., Pellicer, J., Pellissier, L., Pennington, T.D.,
Pérez-Escobar, O.A., Phillips, C., Pironon, S., Possingham, H., Prance,
G., Przelomska, N.A.S., Ramírez-Barahona, S.A., Renner, S.S., Rincon,
M., Rivers, M.C., Rojas Andrés, B.M., Romero-Soler, K.J., Roque, N.,
Rzedowski, J., Sanmartín, I., Santamaría-Aguilar, D., Schellenberger
Costa, D., Serpell, E., Seyfullah, L.J., Shah, T., Shen, X., Silvestro,
D., Simpson, D.A., Šmarda, P., Šmerda, J., Smidt, E., Smith, S.A.,
Solano-Gomez, R., Sothers, C., Soto Gomez, M., Spalink, D., Sperotto,
P., Sun, M., Suz, L.M., Svenning, J.-C., Taylor, A., Tedersoo, L.,
Tietje, M., Trekels, M., Tremblay, R.L., Turner, R., Vasconcelos, T.,
Veselý, P., Villanueva, B.S., Villaverde, T., Vorontsova, M.S., Walker,
B.E., Wang, Z., Watson, M., Weigelt, P., Wenk, E.H., Westrip, J.R.S.,
Wilkinson, T., Willett, S.D., Wilson, K.L., Winter, M., Wirth, C.,
Wölke, F.J.R., Wright, I.J., Zedek, F., Zhigila, D.A., Zimmermann, N.E.,
Zuluaga, A., Zuntini, A.R. (2023). State of the World’s Plants and Fungi
2023. Royal Botanic Gardens, Kew. DOI: https://doi.org/10.34885/wnwn-6s63