Estimates from Surveys | Guesses | % Known and Possible Range | Area (km2) | |||
---|---|---|---|---|---|---|
Survey category | Estimate | ± 95% CL | From | To | ||
Aerial Total Counts | 21,153 | — | — | — | 69.8 | 91,227 |
Individual Registrations | 1,656 | — | — | — | 2.7 | 3,553 |
Informed Guesses | 0 | — | 372 | 439 | 3.4 | 4,465 |
Degraded Data | — | — | 7,651 | 7,651 | 4.2 | 5,466 |
Totals 2015 | 22,809 | 0 | 8,023 | 8,090 | ||
Totals 2006 | 23,994 | 641 | 6,012 | 7,000 | ||
Assessed Range | 80.1 | 104,711 | ||||
Unassessed Range | 19.9 | 26,014 | ||||
Total Range | 100 | 130,725 |
Data Category | Definite | Probable | Possible | Speculative |
---|---|---|---|---|
Aerial or Ground Total Counts | 22,809 | 0 | 0 | 0 |
Informed Guesses | 0 | 0 | 400 | 56 |
Other Guesses | 0 | 0 | 0 | 7,651 |
Totals 2015 | 22,809 | 0 | 400 | 7,707 |
Totals 2006 | 23,353 | 1,316 | 4,946 | 2,021 |
Estimates from Surveys | Guesses | Area | ||||
---|---|---|---|---|---|---|
Cause of Change | Estimate | ± 95% CL | From | To | % Known and Possible | Total |
Repeat Survey | +1,142 | 0 | 0 | 0 | 55.5 | 72,559 |
New Population | +89 | 0 | 0 | 0 | 1.2 | 1,539 |
Different Technique | +779 | 0 | -513 | -476 | 8.1 | 10,548 |
Different Area | -6 | 0 | -100 | -100 | 8.4 | 11,021 |
New Guess | -94 | 0 | -60 | -60 | 2.7 | 3,577 |
Data Degraded | -3,095 | ±641 | +3,095 | +2,137 | 0.0 | 0 |
Totals | -1,185 | ±641 | +2,422 | +1,501 | 75.9 | 104,711 |
Cause of Change | Definite | Probable | Possible | Speculative |
---|---|---|---|---|
Repeat Survey | +1,142 | 0 | 0 | 0 |
New Population | +89 | 0 | 0 | 0 |
Different Technique | +779 | -849 | -360 | +26 |
Different Area | -6 | -50 | -66 | -30 |
New Guess | -94 | -210 | +150 | 0 |
Totals | +1,910 | -1,109 | -276 | -4 |
Data Category | Known Range | Possible Range | Total Range |
---|---|---|---|
Aerial or Ground Total Counts | 93,803 | 977 | 94,780 |
Informed Guesses | 4,465 | 0 | 4,465 |
Other Guesses | 5,423 | 43 | 5,466 |
Unassessed Range | 20,247 | 5,767 | 26,014 |
Totals | 123,937 | 6,787 | 130,725 |
Cause of | Survey Details2 | Number of Elephants | Area | Map Location | |||||||
---|---|---|---|---|---|---|---|---|---|---|---|
Input Zone | Change1 | Type | Reliab. | Year | Estimate | 95% C.L. | Source | PFS3 | (km²) | Lon. | Lat. |
Aberdares | |||||||||||
+ Aberdare National Park | - | O | E | 2005 | 1,840 | 461* | Bitok & Kones, 2005 | 2 | 767 | 36.7E | 0.4S |
+ Aberdare Outside | - | O | E | 2005 | 1,700 | 472* | Bitok & Kones, 2005 | 2 | 663 | 36.7E | 0.6S |
+ Kipipiri Forest Reserve | - | O | E | 2005 | 13 | 25* | Bitok & Kones, 2005 | 3 | 43 | 36.6E | 0.4S |
+ Amboseli Ecosystem | DT | IR | A | 2015 | 1,656 | Fishlock, pers. comm., 2016 | 2 | 5,547 | 37.3E | 2.5S | |
+ Arabuko Sokoke Forest Reserve | - | DC | E | 2002 | 184 | 43 | Litoroh, 2002b | 3 | 415 | 39.9E | 3.3S |
+ Kerio Valley | RS | AT | A | 2015 | 311 | Chase et al., 2016 | 3 | 122 | 36.7E | 0.6N | |
+ Laikipia-Samburu Ecosystem | RS | AT | A | 2012 | 6,365 | Ngene et al., 2013 | 1 | 35,247 | 37.3E | 1.0N | |
+ Lamu District | DA | AT | A | 2015 | 60 | Chase et al., 2016 | 1 | 15,363 | 36.7E | 0.6N | |
+ Loroki Forest | NG | O | D | 2015 | 0 | Thouless, pers. comm., 2016 | 2 | 596 | 36.8E | 1.1N | |
+ Magadi Ecosystem | DT | AT | A | 2013 | 449 | Kenana et al., 2013 | 2 | 6,348 | 36.9E | 2.4S | |
Mara Ecosystem | |||||||||||
+ Masai Mara National Reserve | RS | AT | A | 2014 | 876 | Mduma et al. 2014 | 2 | 1,509 | 35.6E | 1.3S | |
+ Masai Mara Outside | RS | AT | A | 2014 | 532 | Mduma et al. 2014 | 2 | 1,978 | 35.6E | 1.3S | |
+ North Narok Landscape | NP | AT | A | 2014 | 20 | Mduma et al. 2014 | 2 | 310 | 35.9E | 1.1S | |
+ Transmara | DT | O | D | 2015 | 100 | Sitati, pers. comm., 2016 | 3 | 320 | 34.9E | 1.2S | |
+ Marsabit | DT | DC | D | 2014 | 100 | 39 | Kiambi et al., 2014 | 3 | 137 | 38.0E | 2.3N |
+ Mau Forest Complex | - | DC | E | 1995 | 1,003 | Njumbi, et al., 1995 | 2 | 1,267 | 35.5E | 0.5S | |
Meru Ecosystem | |||||||||||
+ Kora National Park | NG | O | D | 2014 | 0 | Kiambi, 2016 | 2 | 1,618 | 38.7E | 0.2S | |
+ Meru National Park and Northwest Bisanadi | DT | AT | A | 2015 | 659 | Chase et al., 2016 | 2 | 1,005 | 36.7E | 0.6N | |
+ Mwingi National Reserve | RS | AT | A | 2007 | 0 | Mwangi et al., 2007 | 3 | 682 | 37.6E | 0.1N | |
+ Rahole National Reserve | NP | AT | A | 2007 | 27 | Mwangi et al., 2007 | 2 | 1,477 | 37.6E | 0.1N | |
+ Southeast Bisanadi National Reserve | DT | O | D | 2014 | 0 | Kiambi, 2016 | 3 | 593 | 38.4E | 0.1N | |
+ Mt Elgon National Park & National Reserve | NG | O | D | 2015 | 200 | Redmond, 2015 | 2 | 1,083 | 34.6E | 1.0N | |
+ Mt Kenya National Park & National Reserve | - | DC | E | 2001 | 2,911 | 640 | Vanleeuwe, 2004 | 2 | 2,007 | 37.4E | 0.2S |
+ Mwea National Reserve | DA | AT | A | 2015 | 71 | Chase et al., 2016 | 4 | 79 | 36.7E | 0.6N | |
+ Nasolot and S. Turkana | RS | AT | A | 2015 | 351 | Chase et al., 2016 | 3 | 581 | 36.7E | 0.6N | |
+ Shimba Hills Ecosystem | DT | AT | A | 2012 | 274 | Ngene & Mukeka, 2012 | 3 | 274 | 39.4E | 4.3S | |
Tsavo Ecosystem | |||||||||||
+ Chyulu National Park | NP | AT | A | 2014 | 42 | Kyale et al., 2014 | 3 | 1,180 | 38.5E | 2.9S | |
+ South Kitui National Reserve | RS | AT | A | 2014 | 0 | Kyale et al., 2014 | 2 | 1,930 | 38.5E | 2.9S | |
+ Tsavo National Park | RS | AT | A | 2014 | 9,504 | Kyale et al., 2014 | 1 | 20,432 | 38.5E | 2.9S | |
+ Tsavo (Outside) | RS | AT | A | 2014 | 1,612 | Kyale et al., 2014 | 1 | 21,081 | 38.5E | 2.9S |
* Range of informed guess
1Key to Causes of Change (only tracked since 2007): DA: Different Area; DD: Data Degraded; DT: Different Technique; NA: New Analysis; NG: New Guess; NP: New population; PL: Population Lost; RS: Repeat Survey (RS ́ denotes a repeat survey that is not statistically comparable for reasons such as different season); –––: No Change
2Key to Survey Types: AC: Aerial Count, not specified; AS: Aerial Sample Count; AT: Aerial Total Count; DC: Dung Count; EX: Extrapolation from GIS; GD: Genetic Dung Count; GS: Ground Sample Count; GT: Ground Total Count; IG: Informed Guess; IR: Individual Registration; OG: Other Guess. Survey Type is followed by an indicator of survey quality, ranked from 1 to 3 (best to worst). Survey Reliability is keyed A-E (best to worst) as outlined in this table.
3PFS: Priority for Future Surveys, ranked from 1 to 5 (highest to lowest). Based on the precision of estimates and the proportion of national range accounted for by the site in question, PFS is a measure of the importance and urgency for future population surveys. All areas of unassessed range have a priority of 1. See Introduction for details on how the PFS is derived.
Note that totals for the Definite, Probable, and Possible categories are derived by pooling the variances of individual estimates, as described at http://www.africanelephantdatabase.org/reliability. As a result, totals do not necessarily match the simple sum of the entries within a given category.