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King Penguin(Aptenodytes patagonicus)

The king penguin stands at 70-100 cm tall and weighs from 9.3-18 kg. Although female and male king penguins are monomorphic they can be separated by their calls. Males are also slightly larger than females. At first glance, the king penguin appears very similar to the larger, closely related emperor penguin, with a broad cheek patch contrasting with surrounding dark feathers and yellow-orange plumage at the top of the chest.

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However, the cheek patch of the adult king penguin is a solid bright orange whereas that of the emperor penguin​ is yellow and white, and the upper chest tends to be more orange and less yellowish in the king species. Both have colourful markings along the side of their lower mandible, but these tend towards pink in emperor penguin and orange in king penguin. Emperor and king penguins typically do not inhabit the same areas in the wild, with the possible exception of vagrants at sea, but the two can readily be distinguished from one another by the king's longer, straighter bill and noticeably sleeker body. The juvenile king penguin with its heavy brown down is completely different in appearance from the mostly grey emperor chick. Once molted of its juvenile plumage, the king chick resembles the adult, but is somewhat less colourful. There are two suspects of king penguin: one is found in the south Atlantic and the other in South Indian Ocean (at the Kerguelen Islands, Crozet Island, Prince Edward Islands and Heard Island and McDonald Islands) and at Macquarie Island.

Habitat

King penguins an be found on most of the subantarctic islands, with the largest colonies now found on Crozet Island (in the southern Indian Ocean), and the islands of Kerguelen, Prince Edward (a Canadian province), and South Georgia (a British Overseas Territory in the southern Atlantic).

Diet

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King penguins eat various species of small fish, squid, and krill. Fish constitute roughly 80% of their diet, except in winter months of July and August, when they make up only around 30%. Lanternfish are the main fish taken,

Breeding

The king penguin is able to breed at three years of age, although only a very small minority actually do then; the average age of first breeding is around 5–6 years. King penguins are serially monogamous. They have only one mate each year, and stay faithful to that mate. However, fidelity between years is less than 30%. The unusually long breeding cycle probably contributes to this low rate. The king penguin has an extremely prolonged breeding cycle, taking around 14–16 months from laying to offspring fledging. Although pairs will attempt to breed annually, they are generally only successful one year in two, or two years in three in a triennial pattern on South Georgia. The reproductive cycle begins in September to November, as birds return to colonies for a prenuptial moult. Those that were unsuccessful in breeding the previous season will usually arrive earlier. They then return to the sea for around three weeks before coming ashore in November or December.

The female penguin lays one pyriform (pear-shaped) white egg weighing 300 g. It is initially soft, but hardens and darkens to a pale greenish colour. It measures around 10 cm × 7 cm. The egg is incubated for around 55 days with both birds sharing incubation in shifts of 6–18 days each. They balance the egg on its feet and incubates it in a brood pouch. Hatching may take up to 2–3 days to complete, and chicks are born semi-altricial and nidicolous. In other words, they have only a thin covering of down, and are entirely dependent on their parents for food and warmth. The guard phase begins with the hatching of the chick. Similar to the emperor penguin, The young king penguin chick spends its time balanced on its parents' feet, sheltered in the brood pouch formed from the abdominal skin of the latter. During this time, the parents alternate every 3–7 days, one guarding the chick while the other forages for food. The guard phase lasts for 30–40 days. By then the chick has grown much larger, and is better able to both keep warm and protect itself against most predators. King chicks are very curious and will wander to explore their surroundings. The chicks form a group, called a  crèche and are watched over by only a few adult birds; most parents leave their chick in these crèches to forage for themselves and their chick. Other species of penguins also practice this method of communal care for offspring.  

By April, the chicks are almost fully grown, but lose weight by fasting over the winter months, gaining it again during spring in September. Fledging then takes place in late spring/early summer.

King penguins form huge breeding colonies; for example, the colony on South Georgia Island at Salisbury Plain holds over 100,000 breeding pairs and the colony at St. Andrew's Bay over 100,000 birds. Because of the very long breeding cycle, colonies are continuously occupied year-round with both adult birds and chicks. During breeding, king penguins do not build nests, however they show strong territorial behaviour and keep a pecking distance to neighbouring penguins. Penguin positions in breeding colonies are highly stable over weeks and appear regularly spaced, but thus far no quantitative analysis of the structural order inside a colony has been performed. The king penguin feeds its chicks by eating fish, digesting it slightly and regurgitating the food into the chick's mouth. Because of their large size, king penguin chicks take 14–16 months before they are ready to go to sea. This is markedly different from smaller penguins, who rear their chicks through a single summer when food is plentiful. King penguins time their mating so the chicks will develop over the harshest season for fishing. In this way, by the time the young penguins are finally mature enough to leave their parents, it is summer when food is plentiful and conditions are more favorable for the young to survive alone at sea.

Population

According to the IUCN Red List, they are classed as Least Concern(LC). Their population trend is classed as increasing. The global population is estimated at 1.1 million annual breeding pairs (range 1,084,320-1,228,320)

Threats

Recent studies showed that sea surface temperatures constitute an important driver of the foraging distribution of this species. The results of modelling imply that the projected southwards shift of the Antarctic Polar Front could have negative consequences for King Penguins as, for at least at some colonies in the Southern Indian Ocean, they would have to travel significantly further to reach their preferred cold water foraging grounds. IPCC climate models suggest that the APF could shift southward 25-40 km per decade, with the northern colonies likely to be more affected than southern ones. The severity of the threat posed by climate change is still unclear, as it may be responsible for recent observed increases, but equally may drive rapid declines over relatively short periods. Similarly, other work on the stability of the APF suggest that the deeper layers may be less prone to movement than surface layers, so that the location of the deep front (and its associated nutrient gradients, strong flow and upwelling) may become decoupled in the future. Furthermore, the depth of the mixed layer may deepen as the Southern Ocean warms and positive Southern Annual Mode (SAM) anomalies occur more frequently. Although there is still uncertainty about how the mixed layer may respond to alterations in the atmosphere, changes in SAM could alter the exchange of heat and carbon between ocean and atmosphere. This in turn has the potential to drive the main prey of King Penguins to greater depths forcing the penguins to dive deeper. Insufficient food may decrease survival of adults. Disease could become an issue in the future as an unknown disease killed 250–300 King Penguins at Marion Island in late October 1992. 
Disturbance from helicopter flights may cause some breeding failure or lead pairs to relocate to alternative breeding sites, and a large scale mortality event associated with aerial logistical operations occurred at Macquarie Island in 1990. Other human impacts could potentially include construction of new science facilities and fisheries, particularly fisheries for myctophid fish if they develop. Oil spills may also be important at local scales. Potential disturbance from tourists, and scientists are  now strictly controlled. Natural predation of chicks by Brown Skua and giant petrels. has a low level of impact on the species. Invasive species may have low-level impacts on King Penguins in parts of the range. Feral cats may depredate chicks (reduced reproductive success), but has no impact on adult mortality . However, cats are present only at a minority of sites, and no population declines have been associated with cat predation. Recent observations in Hogs Island (Crozet) where feral cats are present around the King Penguin colony tend to invalidate that cats could be responsible for the decrease of this major colony. The Argentine Gray Fox is native to much of the southern extreme of south America, but was introduced to Tierra del Fuego island in 1951 in an attempt to control rabbits. Foxes are now causing some chick mortality at newly formed (and increasing) King Penguin colonies. As yet, no assessment has been made of the impact of fox predation, but given that these colonies are increasing and there is no reported adult mortality, it is unlikely to be significant. Rabbits are present at a few sites with potential to impact a small percentage of the global population. Rabbits have now been eradicated from Macquarie and the previous notable impact from herbivory, erosion and landslides on the island, is highly unlikely to recur. No population declines have been attributed to the impact of rabbits.

Conservation

Conservation Actions Underway

The species is the subject of on-going international research but there are currently no special conservation activities.  Human visitation to King penguin colonies is increasing and has the potential to increase disturbance, introduction of non-native species and transmission of disease.  Although many operators have relevant biosecurity procedures in place, there is always a residual risk. 

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Conservation Actions Proposed

Conduct regular surveys to monitor population trends. Continue to improve on existing modelling work to better predict future population changes. Determine the use of marine habitats throughout the annual cycle for breeders and non-breeders. Model foraging habitat to determine the variables that govern distribution. Model foraging responses in years with varying sea surface temperatures. Examine the taxonomic status through population genetics. Instigate disease monitoring and monitor invasive species impact. Management plans must include good biosecurity procedures and preferably also strategies to deal with disease outbreaks and stipulate actions to prevent further spread.

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