To save content items to your account,
please confirm that you agree to abide by our usage policies.
If this is the first time you use this feature, you will be asked to authorise Cambridge Core to connect with your account.
Find out more about saving content to .
To save content items to your Kindle, first ensure no-reply@cambridge.org
is added to your Approved Personal Document E-mail List under your Personal Document Settings
on the Manage Your Content and Devices page of your Amazon account. Then enter the ‘name’ part
of your Kindle email address below.
Find out more about saving to your Kindle.
Note you can select to save to either the @free.kindle.com or @kindle.com variations.
‘@free.kindle.com’ emails are free but can only be saved to your device when it is connected to wi-fi.
‘@kindle.com’ emails can be delivered even when you are not connected to wi-fi, but note that service fees apply.
Polynesia is a hotspot for marine biodiversity in the South Pacific Ocean, yet the distribution of many invertebrate taxa in this region is still often poorly assessed. Information on the diversity and phylogeography of sponges in particular remains limited in spite of their importance for coral reef ecosystems. Recent expeditions to the island group of Wallis and Futuna enabled the first larger-scale assessment of the Wallis Island sponge fauna, resulting in the molecular identification of 82 unique Molecular Operational Taxonomic Units (MOTUs) from 339 sponge samples based on 28S C-region rDNA and CO1 mtDNA data. Faunal comparisons with both adjacent archipelagos and more distant Indo-Pacific regions were predominantly based on the MOTUs obtained from Wallis Island ecoregions, and suggest high levels of endemism of sponges in Wallis and Futuna, corroborating previous data on the biodiversity of sponges and other marine phyla in the South Pacific. The results of this molecular taxonomic survey of the Wallis and Futuna sponge fauna aim to lay solid foundations for a sustainable ‘Blue Economy’ in Wallis and Futuna for the conservation of their local coral reefs.
The bryozoan Uschakovia gorbunovi was initially characterized as a constituent member of benthic communities of the Kara and East-Siberian Seas. The academic literature reports this species in the Barents Sea, but without accurate information on sampling locations. Also, there are no previous records of this species in the northern Greenland Sea near Svalbard. Our analysis of benthic collections obtained during the past two decades revealed the occurrence of four distribution records of Uschakovia gorbunovi within the Barents and Greenland Sea specifying its distribution: one in the northwestern part of the area and three others in the waters surrounding Svalbard. The new distribution records may be related to inadequate sampling efforts or the expansion of this Arctic species into the Barents Sea, which may be due to either natural processes such as ocean currents, or introduction by mobile benthic species such as snow crabs.
Diapterus brevirostris (Sauvage, 1879) is a fish of the family Gerreidae, native to the tropical and subtropical waters of the Pacific coast of America. A specimen of this species was captured off the coast of Asturias, Spain. To the best of our knowledge, this is the first record of the genus Diapterus in the North Atlantic. Given its small size (6.4 cm), it is likely that the species was present in the area for a relatively short time. Although the introduction pathway is unknown, the species' native area and the proximity of a major port to the site of capture suggest that ship's ballast water is the most likely vector of introduction.
In Peter the Great Bay (Russian waters of the Sea of Japan), rhizocephalan barnacle Peltogaster lineata Shiino, 1943, a common parasite of the hermit crab Pagurus brachiomastus (Thallwitz, 1891), was founded for the first time on the hermit crab Pagurus middendorffii Brandt, 1851 (Anomura: Paguridae). Taxonomical identification of the parasite was made using morphological and molecular methods. Pagurus middendorffii is the sixth host of P. lineata.
The brachiopod Argyrotheca cuneata (Brachiopoda: Megathyrididae) is reported for the first time from the southern coast of Türkiye. Twenty-three complete specimens were found in samples of shell grit taken from depths less than 5 m. The findings suggest that A. cuneata may be a common brachiopod species in shallow nearshore habitats along the southern coasts of the country. Widths of the largest and the smallest specimens were 3.7 mm and 0.71 mm, respectively. A comparison of shell dimensions of all specimens indicate an allometric change in the shape of A. cuneata during growth from being longer than wide to wider than long. The protegula preserved on the smallest specimens are described and illustrated possibly for the first time for this species.
The introduction of non-native species is a constant concern around the world since it represents one of the main threats to biodiversity, impacting negatively on native populations, some of them with commercial importance. Hence, monitoring these introductions is fundamental to the management and conservation of the biodiversity of a region. Herein, we report the presence of Moerisia cf. inkermanica in the ballast water of oil tankers loaded at the Cayo Arcas oil terminal. The taxonomy of Moerisia members is uncertain due to the lack of comprehensive morphological descriptions and the few molecular data available. So, we provide a detailed morphological comparison among its congeners. The taxonomic identity of the specimens was determined based on the length of the perradial lobes of the manubrium, the number of tentacles, and the features of their nematocyst rings. Some Moerisids are considered invasive in different localities of the world. However, this genus had not been reported in coastal ecosystems of the Gulf of Mexico over the years until now. Sampled tankers came from different ports of the region, mainly from the northern Gulf of Mexico. Therefore, we encourage systematic monitoring of these ecosystems to recognize the establishment of this species as invasive in the region, know its population dynamics over time, and evaluate the possible ecological impacts that could exert on native populations.
We are all asset managers. Whether as farmers or fishermen, hunters or gatherers, foresters or miners, households or companies, governments or communities, we manage the assets we have access to in line with our motivations, as best as we can. This Review pays close attention to a class of assets we call Nature and studies it in relation to the many other assets in our portfolios.
It is commonly accepted that growing urbanisation accompanying economic growth has created a distance between people and the natural world. There is evidence of that (Chapter 11). Rural communities in low income countries are a lot closer to Nature than are urban households in high income countries.
Chapters 7 and 8 studied externalities that travel in the material world. In fact, externalities are embedded in a larger space. The social world can be as powerful a carrier of externalities as the material environment. A common form in which they appear in the social world is in the way our relationships influence our preferences and wants.
In Chapter 6, aspects of human relationships were studied in terms of the underpinnings of laws and social norms. Here we further probe the factors that are at the heart of human relationships. The features of personhood we examine here will be found to be of special significance for policy, for they tell us about the human motivations that drive population numbers (N) and the standard of living (y), both of which appeared in the Impact Inequality (Chapter 4).
World population in 1950 was around 2.5 billion and global output of final goods and services, at 2011 prices, a little over 9.2 trillion international dollars (dollars at purchasing price parity, PPP) (Figures 4.1 and 4.2). As noted in Chapter 0, the average person’s annual income was about 3,300 dollars PPP, a high figure by historical standards (Maddison, 2018) (Figure 4.3). Since then the world has prospered beyond recognition. Life expectancy at birth in 1950 was 46; today it is above 72. The proportion of the world’s population living in absolute poverty (currently 1.90 dollars PPP a day) has fallen from nearly 60% in 1950 to less than 10% today (World Bank, 2020a). In 2019, the global population had grown to over 7.7 billion even while global income per capita had risen to 15,000 dollars PPP (at 2011 prices).
The Oxford English Dictionary defines institution to be “an established law, custom, usage, practice, organization, or other element in the political or social life of a people”. The present chapter unravels their lead, but recasts the concept so as to stress the role of institutions in economic life.202
By institutions we mean, very loosely, the arrangements that govern collective undertakings. Those arrangements include not only legal entities like the modern firm, but also insurance institutions within village networks, such as the iddir in Ethiopia and variants elsewhere in sub-Saharan Africa (Box 6.4). They include bazaars in the Middle East, village networks for saving and credit in Asia and Latin America, the nuclear household in the West, the extended kinship system of claims and obligations in Africa, and elaborate authority structures such as the Mafia. And they include that overarching entity called government that exists everywhere in the modern world.
In Chapter 10 it was shown that despite wide differences in their foundations, three prominent styles of ethical theory interpret well-being across the generations to be the discounted sum of individual well-beings. We interpreted personal well-being to be the extent to which one’s informed desires are realised, and assumed it is a function of the individual’s standard of living. Realisation of informed desires applies to the cognitive component of happiness (some call it ‘contentment’), but not to the affective component (which can be called the ‘hedonic level of affect’) although it could have a bearing on affect. So, we now dig deeper into the content of well-being.367
In the formal models that were developed in previous chapters, the living standard was represented by the quantity of an all-purpose commodity to which the average person in society has access. We called the all-purpose commodity a consumption good. But the presumption that the sole factor in well-being is consumption may seem otiose.
Mathematical models of economic growth and development could appear esoteric, unreal or even self-indulgent; but they shape, and are in turn shaped by, our conception of humanity’s place in the biosphere. Economists, in planning commissions, ministries of economics and finance, international organisations and private corporations, use the models to analyse data, forecast economic trajectories, evaluate options, and design policy. The economic models that government decision-makers routinely use can be traced directly to academic journals. In turn, economic models in academic journals reflect evolving societal beliefs about what is achievable. The influence is mutual.
Perhaps without conscious design, the macroeconomics of growth and development has been built on the view that human society is external to Nature. In contrast, when constructing the economics of biodiversity, we will keep in mind that we are embedded in it. The difference has profound implications for what we can legitimately expect of the human enterprise.
Restoration seeks to assist Nature recover from a degraded, damaged – even dilapidated – state. Potential benefits from restoring our ecosystems have been discussed earlier in the Review (see in particular Chapter 2). Restored ecosystems are more effective at providing regulating services, which have been lost in many places due to overharvesting of provisioning goods (Chapters 2 and 16). Restoration can make a significant contribution to the mitigation of, and adaptation to, climate change. Successful restoration requires a wider understanding of the relationship between people, Nature and livelihoods, and effective institutions. It relies on sound science, clear objectives, community engagement, monitoring and evaluation (Wortley, Hero, and Howes, 2013; Perring et al. 2015; Gann et al. 2019).