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Nile Crocodile(Crocodylus niloticus)

The Nile crocodile is one of the largest crocodilian species. This reptile is a highly adapted aquatic predator. Females of this species are noticeably smaller than males. The body is streamlined, the tail is long and sturdy, and the hind feet of the animal are webbed. The reptile has long and powerful jaws, which perfectly fit catching and holding the prey. 

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Due to a special valve, found at the back of their throat, these crocodiles can move under water with open mouth, grab and hold prey without ingesting water. The animal has grey-olive body and yellowish belly. Young crocodiles are identified by greenish or dark olive-brown coloration and black colored cross-banding all over the body and tail. As the crocodile grows up, the banding on its body becomes fainter.

Habitat

The Nile crocodile is widely distributed across Sub-Saharan Africa. The reptile most frequently occurs in the central, eastern, and southern regions of Africa as well as Western Madagascar. Being aquatic animal, Nile crocodile is typically found in rivers, large freshwater lakes, freshwater swamps, mangrove swamps as well as coastal estuaries.

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Diet

Being a carnivore, Nile crocodile feeds upon a wide variety of animal species, including insects, amphibians, fish and land mammals such as giraffes or Cape buffaloes. Newly hatched crocodiles usually start with insects, eventually going over to larger prey.

Breeding

Nile crocodiles have polygynous mating system, where one male mates with a number of females. Male crocodiles usually attract receptive females, making a wide variety of noises through bellowing, slapping their snouts in the water or blowing water of out their noses. Meanwhile, larger males are typically more successful in finding mates. The nesting season in this species occurs in November-December. During this period, a female crocodile digs a nest, which is a hole in a river bank or sandy river bed. Then, 25 - 80 eggs are laid and incubated for 80 - 90 days. When the hatching time approaches, the female opens the nest, carrying her offspring to the water. After a while, the young join a crèche of juveniles, which is looked after by females. The hatchlings can remain in this crèche for the first 2 years of their lives. Nile crocodiles are sexually mature at 12 - 16 years old.

Population

According to the IUCN Red List, they are classed as Least Concern(LC). The number of mature individuals is between 50,000 and 70,000 and the population trend is classed as stable.

Threats

Traditional harvesting – In Kenya, the indigenous Pokomo people have eaten crocodile meat and eggs, but the increasing Pokomo population is placing additional pressure on numbers. Uncontrolled use of crocodiles for traditional medicine such as blood, fat, brains and other organs is posing  pressures on some populations.

Human-crocodile conflict – They are a large predator and the recovery of numbers in close proximity to an increasing human population often results in fatal conflicts. 2015 statistics compiled within CrocBITE report 58 fatal and 29 non-fatal attacks. However, reporting of attacks, both fatal and non-fatal, is poor across the range states of C. niloticus, so these numbers are conservative. It has been estimated that over 250 human fatalities occur each year in Kenya alone. Retaliation killings of crocodiles are common across range states.

Land use – They attack cattle as they drink at the water’s edge. In retaliation, Kenyan pastoralists have started to kill crocodiles using pesticide-laced meat in order to preserve their cattle herd. Furthermore, fishermen trap crocodiles with hooks, nets and laced bait and use the crocodile meat as baits for their fish traps, although considerable effort has been made by the Kenya Wildlife Service and the private sector (Nile Crocodiles Ltd) since 2014 to stop this practice. Similar land use pressures are occurring in Botswana, Madagascar (CITES 2016), Namibia, South Africa and Zimbabwe. Larger anthropogenic interference also alters population processes. For example, the Pongolapoort Dam in Ndumo Game Reserve, completed in 1972, allows artificial control of water flow rates and subsequent flooding. One consequence is that during flood events, the natural watercourse is diverted away from historical nesting grounds.

Food – unregulated or illegal overfishing in many range states is depleting fish stocks, which could have detrimental effects on populations.

 

Pollution – Increased nutrient and sediment profiles of the water column of the Olifants River, South Africa due to upstream mining, industrial and agricultural activities, and urbanisation. These have caused isolated large-scale fish mortality incidents. Histopathological investigation of dead crocodiles were found to have fed on these dead fish and succumbed to pansteatitis. Additional mining leases have been granted in the upper Olifants River and unless environmental protection mechanisms are implemented, the aquatic health may continue to decline. Similar pollution concerns are being raised in the South East Lowveld region in Zimbabwe, where rivers flow through large sugar plantations and fish health is starting to decline due to contamination with agricultural chemicals and fertilisers. Lead uptake by the ingestion of fishing sinkers has also been reported.

Invasive weeds – In 2001 it was reported that the invasive Triffid/Siam Weed, Chromolaena odorata, is found in Lake St. Lucia within the iSimangaliso (previously Greater St. Lucia) Wetland Park in South Africa. The weed could be detrimental in a number of ways. First, it was noted that many females were trying to dig holes to lay their eggs but could not dig through the fibrous root mats. Second, if the roots could be avoided, Chromolaena odorata shaded the nests reducing their average temperature by 5-6oC cooler relative to sun-exposed nests. Like all crocodilians, sex ratios  are determined by incubation temperature and nests shaded. Furthermore, as in other crocodilian species, hatchlings resulting from less than ideal incubation conditions can have a higher frequency of abnormalities, in addition to influences on post-hatching body size, residual yolk mass, growth and thermoregulatory behaviour. The worst case scenario is complete embryonic developmental failure (death) due to sub-optimal temperatures. Ezemvelo KZN Wildlife, the provincial conservation agency, have a programme to annually eradicate C. odorata from known nesting areas along the Mphathe Stream a few months prior to crocodile nesting. It was found that females do return to cleared sites for oviposition.

Habitat destruction – The habitat of Nile Crocodiles is being modified in numerous ways. For example, the Lake Flag Boshielo dam wall (South Africa) was raised by five meters in 2005 and the resultant rise in water level flooded the existing basking sites of the resident population; within four years the population had decreased from 135 individuals to 98, which was also reflected in the adult population. A similar situation was reported in the Ndumo Game Reserve (South Africa) after the construction of Pongolapoort Dam, which artificially controls water flow rates and subsequent flooding that has diverted the natural watercourse away from historical nesting grounds. In contrast, the construction of the Aswan Dam, Egypt have led to population expansions of Nile crocodiles there. Another example of habitat destruction is in Kenya and Madagascar where people are moving towards the river to cut out small plots to live and grow crops, leading not only reduced crocodile (nesting) habitat but exacerbating human-crocodile conflicts. Other habitat loss includes siltation of rivers due to anthropogenic factors such as clearing, burning and subsequent erosion.

Conservation

High priority
 

1. Population survey data is urgently needed for most countries to quantify regional status and determine objectively whether management activities, be they restricted to protection or involving sustainable use, are achieving their conservation goals. Such assessments and survey data provide an evidence-base for developing conservation and management programs in some nations.
2. Innovative approaches to raise awareness of the intrinsic and non-consumptive value of crocodiles and their management, as perceived by national authorities, are needed to prioritize crocodile conservation particularly in light of the value given to more charismatic species such as elephant, large primates and the big cats.
3. Study of human-crocodile conflict impacts, mitigation and “problem crocodile” management programs is central to Crocodylus niloticus conservation in most countries. Conflict between rural communities and crocodiles is the primary concern in the management of the wild crocodile population in many African countries. The problems are poorly understood for many reasons, including the lack of systematic recording of incidents and their context, with CrocBITE (2013) providing a valuable pioneering role. Technologies to reduce the probability of crocodile attacks exist but are limited in scope and livelihood context. In countries such as Madagascar, where mitigation nominally involves the removal of crocodiles and the commercial use of their skins, the efficacy of the program and impact on the depleted wild populations needs to be assessed objectively.
4. Impact of anthropogenic contaminants, with particular attention to the South African population. Much of the South African population appears to be at risk from contamination, with large-scale die-offs documented in prominent conservation areas (e.g. Loskop Dam Nature Reserve and Kruger National Park) since 2005. Populations in St. Lucia may not be secure, with agriculture, industry (sugarcane) and human settlements in the catchment on the increase.
5. Further delineation between the ranges of C. niloticus and C. suchus is required to ensure the action plans are specific for each species. 

Moderate priority

6. Allocation/demarcation of locally protected areas. They looked at nest site habitat suitability versus available habitat in the Okavango Delta, Botswana. These data were then overlaid to produce a map with priority areas for nesting that led to the establishment of a nesting sanctuary for C. niloticus. This process could be repeated in other national contexts.
7. Facilitation of management programs for countries planning or implementing sustainable utilization. A number of African nations lack the appropriate policy environment, management capability and technical expertise to plan and/or implement use programs, added to the often complex social, economic and biological variables involved. Another tier lies in a commitment to adaptive rather than strictly prescriptive management, Population surveys, monitoring, data assessment, technique training, reporting and incentives are needed to foster and sustain these programs. Hutton (1990) outlined some priority areas that need to be addressed for the development of sustainable use programs in the African context:
a.  Pre-feasibility studies (e.g. harvest potential);b.  Policy and legislation to provide a management framework;
c.  Feasibility studies (identification of potential production sites, evaluation and quantification of factors inherent in sustainable use programs);
d.  International requirements for trade (CITES submissions, documentation and tagging of hides);
e.  Population census and monitoring (technical support and training);
f.  Technical support for developing ranching/farming programs; and,
g.  Marketing.

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