Ugalla - Revision history

WikiEdit at 21:55, 15 October 2026

2026-10-15T21:55:07Z

← Older revision		Revision as of 17:55, 15 October 2026
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	<span id="R01858"></span>Ogawa, H., Idani, G., Moore, J., Pintea, L., & Hernandez-Aguilar, A. (2007). Sleeping Parties and Nest Distribution of Chimpanzees in the Savanna Woodland, Ugalla, Tanzania. ''International Journal of Primatology'', 28(6), 1397-1412. [https://doi.org/10.1007/s10764-007-9210-0 doi:10.1007/s10764-007-9210-0]		<span id="R01858"></span>Ogawa, H., Idani, G., Moore, J., Pintea, L., & Hernandez-Aguilar, A. (2007). Sleeping Parties and Nest Distribution of Chimpanzees in the Savanna Woodland, Ugalla, Tanzania. ''International Journal of Primatology'', 28(6), 1397-1412. [https://doi.org/10.1007/s10764-007-9210-0 doi:10.1007/s10764-007-9210-0]

	<span id="R02334"></span>Kiribou, R., Tehoda, P., Chukwu, O., Bempah, G., Kühl, H. S., Ferreira, J., …, & Heinicke, S. (2024). Exposure of African ape sites to climate change impacts. ''PLOS Climate'', 3(2), ~~1-19~~. [https://doi.org/10.1371/journal.pclm.0000345 doi:10.1371/journal.pclm.0000345]		<span id="R02334"></span>Kiribou, R., Tehoda, P., Chukwu, O., Bempah, G., Kühl, H. S., Ferreira, J., …, & Heinicke, S. (2024). Exposure of African ape sites to climate change impacts. ''PLOS Climate'', 3(2), e0000345. [https://doi.org/10.1371/journal.pclm.0000345 doi:10.1371/journal.pclm.0000345]



	'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14		'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14

WikiEdit at 14:36, 15 October 2026

2026-10-15T14:36:15Z

← Older revision		Revision as of 10:36, 15 October 2026
Line 354:		Line 354:
	<span id="R01858"></span>Ogawa, H., Idani, G., Moore, J., Pintea, L., & Hernandez-Aguilar, A. (2007). Sleeping Parties and Nest Distribution of Chimpanzees in the Savanna Woodland, Ugalla, Tanzania. ''International Journal of Primatology'', 28(6), 1397-1412. [https://doi.org/10.1007/s10764-007-9210-0 doi:10.1007/s10764-007-9210-0]		<span id="R01858"></span>Ogawa, H., Idani, G., Moore, J., Pintea, L., & Hernandez-Aguilar, A. (2007). Sleeping Parties and Nest Distribution of Chimpanzees in the Savanna Woodland, Ugalla, Tanzania. ''International Journal of Primatology'', 28(6), 1397-1412. [https://doi.org/10.1007/s10764-007-9210-0 doi:10.1007/s10764-007-9210-0]

	<span id="R02334"></span>Kiribou, R., Tehoda, P., Chukwu, O., Bempah, G., Kühl, H. S., Ferreira, J., …, & Heinicke, S. (2024). Exposure of African ape sites to climate change impacts. ''PLOS Climate'', 3(2), ~~e0000345~~. [https://doi.org/10.1371/journal.pclm.0000345 doi:10.1371/journal.pclm.0000345]		<span id="R02334"></span>Kiribou, R., Tehoda, P., Chukwu, O., Bempah, G., Kühl, H. S., Ferreira, J., …, & Heinicke, S. (2024). Exposure of African ape sites to climate change impacts. ''PLOS Climate'', 3(2), 1-19. [https://doi.org/10.1371/journal.pclm.0000345 doi:10.1371/journal.pclm.0000345]



	'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14		'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14

WikiEdit at 19:13, 14 October 2026

2026-10-14T19:13:16Z

← Older revision		Revision as of 15:13, 14 October 2026
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	<span id="R01855"></span>Hernandez-Aguilar, R. A., Moore, J., & Pickering, T. R. (2007). Savanna chimpanzees use tools to harvest the underground storage organs of plants. ''Proceedings of the National Academy of Sciences'', 104(49), 19210-19213. [https://doi.org/10.1073/pnas.0707929104 doi:10.1073/pnas.0707929104]		<span id="R01855"></span>Hernandez-Aguilar, R. A., Moore, J., & Pickering, T. R. (2007). Savanna chimpanzees use tools to harvest the underground storage organs of plants. ''Proceedings of the National Academy of Sciences'', 104(49), 19210-19213. [https://doi.org/10.1073/pnas.0707929104 doi:10.1073/pnas.0707929104]

	<span id="R01856"></span>Masanja, G. F. (2014). Human population growth and wildlife extinction in Ugalla ecosystem, western Tanzania. Journal of Sustainable Development Studies, 5(2).		<span id="R01856"></span>Masanja, G. F. (2014). Human population growth and wildlife extinction in Ugalla ecosystem, western Tanzania. Journal of Sustainable Development Studies, 5(2). [http://infinitypress.info/index.php/jsds/article/view/596 link]

	<span id="R01857"></span>Moore, D. L., & Vigilant, L. (2014). A population estimate of chimpanzees (Pan troglodytes schweinfurthii) in the Ugalla region using standard and spatially explicit genetic capture–recapture methods. American Journal of Primatology, 76(4), 335–346. [https://doi.org/10.1002/ajp.22237 doi:10.1002/ajp.22237]		<span id="R01857"></span>Moore, D. L., & Vigilant, L. (2014). A population estimate of chimpanzees (Pan troglodytes schweinfurthii) in the Ugalla region using standard and spatially explicit genetic capture–recapture methods. American Journal of Primatology, 76(4), 335–346. [https://doi.org/10.1002/ajp.22237 doi:10.1002/ajp.22237]

WikiEdit at 20:31, 12 October 2026

2026-10-12T20:31:33Z

← Older revision		Revision as of 16:31, 12 October 2026
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	= Site characteristics =		= Site characteristics =

	The Ugalla region is located approximately 65 km east of Lake Tanganyika, in western Tanzania (Moore & Vigilant 2014). A large part of the region is found within the East Tongwe Forest Reserve and is not part of the national park system of Tanzania (Moore & Vigilant 2014). The site covers approximately 3,350 sq.km and is one of the most seasonal, dry, and open chimpanzee habitats (Moore & Vigilant 2014). The region is classified as savanna-woodland; the grassy groundcover is extensive, the drought season takes place between May and October, and there is minimal rainfall. Small strips of forest occur around the ephemeral rivers of Ugalla (Moore & Vigilant 2014).		The Ugalla region is located approximately 65 km east of Lake Tanganyika, in western Tanzania ([[#R01857\|Moore & Vigilant 2014]]). A large part of the region is found within the East Tongwe Forest Reserve and is not part of the national park system of Tanzania ([[#R01857\|Moore & Vigilant 2014]]). The site covers approximately 3,350 sq.km and is one of the most seasonal, dry, and open chimpanzee habitats ([[#R01857\|Moore & Vigilant 2014]]). The region is classified as savanna-woodland; the grassy groundcover is extensive, the drought season takes place between May and October, and there is minimal rainfall. Small strips of forest occur around the ephemeral rivers of Ugalla ([[#R01857\|Moore & Vigilant 2014]]).

	'''Table 1. Basic site information for Ugalla'''		'''Table 1. Basic site information for Ugalla'''
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	\|Reconnaissance walk		\|Reconnaissance walk
	\|		\|
	\|Moore & Vigilant 2014		\|[[#R01857\|Moore & Vigilant 2014]]
	\|Standard and spatially explicit genetic capture-recapture methods		\|Standard and spatially explicit genetic capture-recapture methods
	\|		\|
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	\|Line transects & recces		\|Line transects & recces
	\|		\|
	\|Ogawa et al. 2007		\|[[#R01858\|Ogawa et al. 2007]]
	\|		\|
	\|		\|
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	= Threats =		= Threats =

	The area has been under increasing pressure from human disturbance. The greatest threats include agricultural expansion, cattle herding, fire, logging, and poaching (Masanja 2014). Hunting with snares is very common, but large game such as buffalo (''Syncerus caffer''), rhinoceros (''Diceros bicornis'') or elephant (''Loxodonta africana'') are hunted with firearms. Elephant, rhinoceros and lion numbers have declined sharply in Ugalla, along with increased illegal ivory trade (Masanja 2014).		The area has been under increasing pressure from human disturbance. The greatest threats include agricultural expansion, cattle herding, fire, logging, and poaching ([[#R01856\|Masanja 2014]]). Hunting with snares is very common, but large game such as buffalo (''Syncerus caffer''), rhinoceros (''Diceros bicornis'') or elephant (''Loxodonta africana'') are hunted with firearms. Elephant, rhinoceros and lion numbers have declined sharply in Ugalla, along with increased illegal ivory trade ([[#R01856\|Masanja 2014]]).

	'''Table 3. Threats to apes reported for Ugalla'''		'''Table 3. Threats to apes reported for Ugalla'''
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	\|5.1 Hunting & collecting terrestrial animals		\|5.1 Hunting & collecting terrestrial animals
	\|High (more than 70% of population affected)		\|High (more than 70% of population affected)
	\|Poaching is a serious problem in Ugalla because of poverty and a massive increase in demand for animal protein (Masanja 2014).		\|Poaching is a serious problem in Ugalla because of poverty and a massive increase in demand for animal protein ([[#R01856\|Masanja 2014]]).
	\|Ongoing (2014)		\|Ongoing (2014)
	\|-		\|-
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	\|7.1 Fire & fire suppression		\|7.1 Fire & fire suppression
	\|Present (unknown severity)		\|Present (unknown severity)
	\|People burn grassland during the dry season. Although the fires have direct and indirect influences on vegetation and wild animals, trees don't die from the fires; the woodland in the area is considered fire-adapted (Ogawa 2007).		\|People burn grassland during the dry season. Although the fires have direct and indirect influences on vegetation and wild animals, trees don't die from the fires; the woodland in the area is considered fire-adapted ([[#R01858\|Ogawa 2007]]).
	\|Ongoing (2007)		\|Ongoing (2007)
	\|}		\|}
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	= Research activities =		= Research activities =

	A behavioral study of chimpanzees at the site documented the use of tools to dig for plant underground storage organs (USOs), suggesting that exploitation of such resources was within the cognitive and technological reach of the earliest hominins (Hernandez-Aguilar, Moore & Pickering 2007).		A behavioral study of chimpanzees at the site documented the use of tools to dig for plant underground storage organs (USOs), suggesting that exploitation of such resources was within the cognitive and technological reach of the earliest hominins ([[#R01855\|Hernandez-Aguilar, Moore & Pickering 2007]]).


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	\|		\|
	\|		\|
	\|Hernandez-Aguilar, Moore & Pickering 2007		\|[[#R01855\|Hernandez-Aguilar, Moore & Pickering 2007]]
	\|		\|
	\|		\|
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	= Exposure to climate change impacts =		= Exposure to climate change impacts =

	As part of a study on the exposure of African great ape sites to climate change impacts, Kiribou et al. (2024) extracted climate data and data on projected extreme climate impact events for the site. Climatological characteristics were derived from observation-based climate data provided by the Inter-Sectoral Impact Model Intercomparison Project (ISIMIP, www.isimip.org). Parameters were calculated as the average across each 30-year period. For 1981-2010, the EWEMBI dataset from ISIMIP2a was used. For the two future periods (2021-2050 and 2071-2099) ISIMIP2b climate data based on four CMIP5 global climate models were used. For future projections, two Representative Concentration Pathways (RCP) were used. RCP 2.6 is a scenario with strong mitigation measures in which global temperatures would likely rise below 2C. RCP 6.0 is a scenario with medium emissions in which global temperatures would likely rise up to 3C by 2100. For the number of days with heavy precipitation events, the 98th percentile of all precipitation days (>1mm/d) was calculated for the 1979-2013 reference period as a threshold for a heavy precipitation event. Then, for each year, the number of days above that threshold was derived. The figures on temperature and precipitation anomaly show the deviation from the mean temperature and mean precipitation for the 1979-2013 reference period.		As part of a study on the exposure of African great ape sites to climate change impacts, [[#R02334\|Kiribou et al. (2024)]] extracted climate data and data on projected extreme climate impact events for the site. Climatological characteristics were derived from observation-based climate data provided by the Inter-Sectoral Impact Model Intercomparison Project (ISIMIP, www.isimip.org). Parameters were calculated as the average across each 30-year period. For 1981-2010, the EWEMBI dataset from ISIMIP2a was used. For the two future periods (2021-2050 and 2071-2099) ISIMIP2b climate data based on four CMIP5 global climate models were used. For future projections, two Representative Concentration Pathways (RCP) were used. RCP 2.6 is a scenario with strong mitigation measures in which global temperatures would likely rise below 2C. RCP 6.0 is a scenario with medium emissions in which global temperatures would likely rise up to 3C by 2100. For the number of days with heavy precipitation events, the 98th percentile of all precipitation days (>1mm/d) was calculated for the 1979-2013 reference period as a threshold for a heavy precipitation event. Then, for each year, the number of days above that threshold was derived. The figures on temperature and precipitation anomaly show the deviation from the mean temperature and mean precipitation for the 1979-2013 reference period.

	The estimated exposure to future extreme climate impact events (crop failure, drought, river flood, wildfire, tropical cyclone, and heatwave) is based on a published dataset by Lange et al. 2020 derived from ISIMIP2b data. The same global climate models and RCPs as described above were used. Within each 30-year period, the number of years with an extreme event and the average proportion of the site affected were calculated (Kiribou et al. 2024).		The estimated exposure to future extreme climate impact events (crop failure, drought, river flood, wildfire, tropical cyclone, and heatwave) is based on a published dataset by Lange et al. 2020 derived from ISIMIP2b data. The same global climate models and RCPs as described above were used. Within each 30-year period, the number of years with an extreme event and the average proportion of the site affected were calculated ([[#R02334\|Kiribou et al. 2024]]).

	'''Table 8. Estimated past and projected climatological characteristics in Ugalla'''		'''Table 8. Estimated past and projected climatological characteristics in Ugalla'''
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	= References =		= References =

	Hernandez-Aguilar, R. A., Moore, J., & Pickering, T. R. (2007). Savanna chimpanzees use tools to harvest the underground storage organs of plants. Proceedings of the National Academy of Sciences, 104(49), ~~19210–19213~~. ~~<br>~~		<span id="R01855"></span>Hernandez-Aguilar, R. A., Moore, J., & Pickering, T. R. (2007). Savanna chimpanzees use tools to harvest the underground storage organs of plants. ''Proceedings of the National Academy of Sciences'', 104(49), 19210-19213. [https://doi.org/10.1073/pnas.0707929104 doi:10.1073/pnas.0707929104]

	Masanja, G. F. (2014). Human population growth and wildlife extinction in Ugalla ecosystem, western Tanzania. Journal of Sustainable Development Studies, 5(2). ~~<br>~~		<span id="R01856"></span>Masanja, G. F. (2014). Human population growth and wildlife extinction in Ugalla ecosystem, western Tanzania. Journal of Sustainable Development Studies, 5(2).

	Moore, D. L., & Vigilant, L. (2014). A population estimate of chimpanzees (Pan troglodytes schweinfurthii) in the Ugalla region using standard and spatially explicit genetic capture–recapture methods. American Journal of Primatology, 76(4), 335–346. ~~<br>~~		<span id="R01857"></span>Moore, D. L., & Vigilant, L. (2014). A population estimate of chimpanzees (Pan troglodytes schweinfurthii) in the Ugalla region using standard and spatially explicit genetic capture–recapture methods. American Journal of Primatology, 76(4), 335–346. [https://doi.org/10.1002/ajp.22237 doi:10.1002/ajp.22237]

	Ogawa, H., Moore, J., Pintea, L., & Hernandez-Aguilar, A. (2007). Sleeping ~~parties~~ and ~~nest distribution~~ of ~~chimpanzees~~ in the ~~savanna woodland~~, Ugalla, Tanzania. International Journal of Primatology, 28(6), ~~1397–1412~~. <br>		<span id="R01858"></span>Ogawa, H., Idani, G., Moore, J., Pintea, L., & Hernandez-Aguilar, A. (2007). Sleeping Parties and Nest Distribution of Chimpanzees in the Savanna Woodland, Ugalla, Tanzania. ''International Journal of Primatology'', 28(6), 1397-1412. [https://doi.org/10.1007/s10764-007-9210-0 doi:10.1007/s10764-007-9210-0]

			<span id="R02334"></span>Kiribou, R., Tehoda, P., Chukwu, O., Bempah, G., Kühl, H. S., Ferreira, J., …, & Heinicke, S. (2024). Exposure of African ape sites to climate change impacts. ''PLOS Climate'', 3(2), e0000345. [https://doi.org/10.1371/journal.pclm.0000345 doi:10.1371/journal.pclm.0000345]



	'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14		'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14

WikiEdit at 12:21, 3 September 2026

2026-09-03T12:21:05Z

← Older revision		Revision as of 08:21, 3 September 2026
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	= Exposure to climate change impacts =		= Exposure to climate change impacts =

	As part of a study on the exposure of African great ape sites to climate change impacts, Kiribou et al. ~~subm.~~ extracted climate data and data on projected extreme climate impact events for the site. Climatological characteristics were derived from observation-based climate data provided by the Inter-Sectoral Impact Model Intercomparison Project (ISIMIP, www.isimip.org). Parameters were calculated as the average across each 30-year period. For 1981-2010, the EWEMBI dataset from ISIMIP2a was used. For the two future periods (2021-2050 and 2071-2099) ISIMIP2b climate data based on four CMIP5 global climate models were used. For future projections, two Representative Concentration Pathways (RCP) were used. RCP 2.6 is a scenario with strong mitigation measures in which global temperatures would likely rise below 2C. RCP 6.0 is a scenario with medium emissions in which global temperatures would likely rise up to 3C by 2100. For the number of days with heavy precipitation events, the 98th percentile of all precipitation days (>1mm/d) was calculated for the 1979-2013 reference period as a threshold for a heavy precipitation event. Then, for each year, the number of days above that threshold was derived. The figures on temperature and precipitation anomaly show the deviation from the mean temperature and mean precipitation for the 1979-2013 reference period.		As part of a study on the exposure of African great ape sites to climate change impacts, Kiribou et al. (2024) extracted climate data and data on projected extreme climate impact events for the site. Climatological characteristics were derived from observation-based climate data provided by the Inter-Sectoral Impact Model Intercomparison Project (ISIMIP, www.isimip.org). Parameters were calculated as the average across each 30-year period. For 1981-2010, the EWEMBI dataset from ISIMIP2a was used. For the two future periods (2021-2050 and 2071-2099) ISIMIP2b climate data based on four CMIP5 global climate models were used. For future projections, two Representative Concentration Pathways (RCP) were used. RCP 2.6 is a scenario with strong mitigation measures in which global temperatures would likely rise below 2C. RCP 6.0 is a scenario with medium emissions in which global temperatures would likely rise up to 3C by 2100. For the number of days with heavy precipitation events, the 98th percentile of all precipitation days (>1mm/d) was calculated for the 1979-2013 reference period as a threshold for a heavy precipitation event. Then, for each year, the number of days above that threshold was derived. The figures on temperature and precipitation anomaly show the deviation from the mean temperature and mean precipitation for the 1979-2013 reference period.

	The estimated exposure to future extreme climate impact events (crop failure, drought, river flood, wildfire, tropical cyclone, and heatwave) is based on a published dataset by Lange et al. 2020 derived from ISIMIP2b data. The same global climate models and RCPs as described above were used. Within each 30-year period, the number of years with an extreme event and the average proportion of the site affected were calculated (~~see~~ Kiribou et al. ~~subm. for details~~).		The estimated exposure to future extreme climate impact events (crop failure, drought, river flood, wildfire, tropical cyclone, and heatwave) is based on a published dataset by Lange et al. 2020 derived from ISIMIP2b data. The same global climate models and RCPs as described above were used. Within each 30-year period, the number of years with an extreme event and the average proportion of the site affected were calculated (Kiribou et al. 2024).

	'''Table 8. Estimated past and projected climatological characteristics in Ugalla'''		'''Table 8. Estimated past and projected climatological characteristics in Ugalla'''

WikiEdit at 14:51, 1 September 2026

2026-09-01T14:51:32Z

← Older revision		Revision as of 10:51, 1 September 2026
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	!Comments		!Comments
	!A.P.E.S. database ID		!A.P.E.S. database ID
			\|-
			\|''Pan troglodytes schweinfurthii''
			\|2009-2010
			\|
			\|
			\|0.25 (0.16-0.38)
			\|322 (227-373)
			\|Ugalla region (624 km²)
			\|Reconnaissance walk
			\|
			\|Moore & Vigilant 2014
			\|Standard and spatially explicit genetic capture-recapture methods
			\|
	\|-		\|-
	\|''Pan troglodytes schweinfurthii''		\|''Pan troglodytes schweinfurthii''
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	\|Ogawa et al. 2007		\|Ogawa et al. 2007
	\|		\|
	\|
	\|-
	~~\|''Pan troglodytes schweinfurthii''~~
	~~\|2009-2010~~
	\|
	\|
	~~\|0.25 (0.16-0.38)~~
	~~\|322 (227-373)~~
	~~\|Ugalla region (624 km²)~~
	~~\|Reconnaissance walk~~
	\|
	~~\|Moore & Vigilant 2014~~
	~~\|Standard and spatially explicit genetic capture-recapture methods~~
	\|		\|
	\|}		\|}
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	= References =		= References =

	Moore, ~~D. L~~., & ~~Vigilant~~, L. (~~2014~~). ~~A population estimate of~~ chimpanzees ~~(Pan troglodytes schweinfurthii) in~~ the ~~Ugalla region using standard and spatially explicit genetic capture–recapture methods~~. ~~American Journal~~ of ~~Primatology~~, 76(4), ~~335-346~~.		Hernandez-Aguilar, R. A., Moore, J., & Pickering, T. R. (2007). Savanna chimpanzees use tools to harvest the underground storage organs of plants. Proceedings of the National Academy of Sciences, 104(49), 19210–19213. <br>

	~~Ogawa~~, H.~~, Moore, J., Pintea, L., & Hernandez-Aguilar, A~~. (~~2007~~). ~~Sleeping parties~~ and ~~nest distribution of chimpanzees~~ in ~~the savanna woodland,~~ Ugalla, Tanzania. ~~International~~ Journal of ~~Primatology~~, 28(6)~~, 1397-1412~~.		Masanja, G. F. (2014). Human population growth and wildlife extinction in Ugalla ecosystem, western Tanzania. Journal of Sustainable Development Studies, 5(2). <br>

	~~Hernandez-Aguilar~~, R. ~~A., Moore, J~~., & ~~Pickering~~, ~~T. R~~. (~~2007~~). ~~Savanna~~ chimpanzees ~~use tools to harvest~~ the ~~underground storage organs of plants~~. ~~Proceedings of the National Academy~~ of ~~Sciences~~, ~~104~~(49), ~~19210-19213~~.		Moore, D. L., & Vigilant, L. (2014). A population estimate of chimpanzees (Pan troglodytes schweinfurthii) in the Ugalla region using standard and spatially explicit genetic capture–recapture methods. American Journal of Primatology, 76(4), 335–346. <br>

	~~Masanja~~, G. F. (~~2014~~). ~~Human population growth~~ and ~~wildlife extinction~~ in Ugalla ~~ecosystem~~, ~~western~~ Tanzania. Journal of ~~Sustainable Development Studies~~, 5(2).		Ogawa, H., Moore, J., Pintea, L., & Hernandez-Aguilar, A. (2007). Sleeping parties and nest distribution of chimpanzees in the savanna woodland, Ugalla, Tanzania. International Journal of Primatology, 28(6), 1397–1412. <br>



	'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14		'''Page created by: '''APES Atlas Team''' Date:''' 2021-11-14

WikiEdit at 14:49, 25 March 2026

2026-03-25T14:49:59Z

← Older revision		Revision as of 10:49, 25 March 2026
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	* Key threats to chimpanzees are poaching and habitat encroachment.		* Key threats to chimpanzees are poaching and habitat encroachment.
	* Conservation activities are not documented.		* Conservation activities are not documented.






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	!Description		!Description
	!Year of threat		!Year of threat
			\|-
			\|5 Biological resource use
			\|5.1 Hunting & collecting terrestrial animals
			\|High (more than 70% of population affected)
			\|Poaching is a serious problem in Ugalla because of poverty and a massive increase in demand for animal protein (Masanja 2014).
			\|Ongoing (2014)
	\|-		\|-
	\|7 Natural system modifications		\|7 Natural system modifications
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	\|People burn grassland during the dry season. Although the fires have direct and indirect influences on vegetation and wild animals, trees don't die from the fires; the woodland in the area is considered fire-adapted (Ogawa 2007).		\|People burn grassland during the dry season. Although the fires have direct and indirect influences on vegetation and wild animals, trees don't die from the fires; the woodland in the area is considered fire-adapted (Ogawa 2007).
	\|Ongoing (2007)		\|Ongoing (2007)
	\|-
	~~\|5 Biological resource use~~
	~~\|5.1 Hunting & collecting terrestrial animals~~
	~~\|High (more than 70% of population affected)~~
	~~\|Poaching is a serious problem in Ugalla because of poverty and a massive increase in demand for animal protein (Masanja 2014).~~
	~~\|Ongoing (2014)~~
	\|}		\|}

WikiEdit at 07:11, 6 November 2025

2025-11-06T07:11:51Z

← Older revision		Revision as of 03:11, 6 November 2025
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	<div><ul><li style="display: inline-block; vertical-align: top;"> [[File:PrecipAnomaly_Ugalla_Deborah_Moore.png\| 450px \| thumb\| none \| Precipitation anomaly ~~inUgalla~~]] </li><li style="display: inline-block; vertical-align: top;"> [[File:TempAnomaly_Ugalla_Deborah_Moore.png \| 450px \| thumb\| none \| Temperature anomaly ~~inUgalla~~]] </li></ul></div>		<div><ul><li style="display: inline-block; vertical-align: top;"> [[File:PrecipAnomaly_Ugalla_Deborah_Moore.png\| 450px \| thumb\| none \| Precipitation anomaly in Ugalla]] </li><li style="display: inline-block; vertical-align: top;"> [[File:TempAnomaly_Ugalla_Deborah_Moore.png \| 450px \| thumb\| none \| Temperature anomaly in Ugalla]] </li></ul></div>

	= External links =		= External links =

WikiEdit at 06:55, 6 November 2025

2025-11-06T06:55:48Z

← Older revision		Revision as of 02:55, 6 November 2025
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	* Key threats to chimpanzees are poaching and habitat encroachment.		* Key threats to chimpanzees are poaching and habitat encroachment.
	* Conservation activities are not documented.		* Conservation activities are not documented.



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	[[Types of sites]] [[Governance types]] [[Habitat types]]		[[Types of sites]] [[Governance types]] [[Habitat types]]

	= Ape status =		= Ape status =

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	[[Sampling methods]] [[Analytical frameworks]]		[[Sampling methods]] [[Analytical frameworks]]

	= Threats =		= Threats =

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	[[Threats]]		[[Threats]]

	= Conservation activities =		= Conservation activities =



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	[[Challenges]]		[[Challenges]]

	= Enablers =		= Enablers =

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	[[Enablers]]		[[Enablers]]

	= Research activities =		= Research activities =

	A behavioral study of chimpanzees at the site documented the use of tools to dig for plant underground storage organs (USOs), suggesting that exploitation of such resources was within the cognitive and technological reach of the earliest hominins (Hernandez-Aguilar, Moore & Pickering 2007).		A behavioral study of chimpanzees at the site documented the use of tools to dig for plant underground storage organs (USOs), suggesting that exploitation of such resources was within the cognitive and technological reach of the earliest hominins (Hernandez-Aguilar, Moore & Pickering 2007).


	= Documented behaviours =		= Documented behaviours =
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	[[Behaviours]]		[[Behaviours]]

	= Exposure to climate change impacts =		= Exposure to climate change impacts =

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	\|}		\|}


			<div><ul><li style="display: inline-block; vertical-align: top;"> [[File:PrecipAnomaly_Ugalla_Deborah_Moore.png\| 450px \| thumb\| none \| Precipitation anomaly inUgalla]] </li><li style="display: inline-block; vertical-align: top;"> [[File:TempAnomaly_Ugalla_Deborah_Moore.png \| 450px \| thumb\| none \| Temperature anomaly inUgalla]] </li></ul></div>

	= External links =		= External links =

WikiEdit at 08:18, 31 October 2025

2025-10-31T08:18:13Z

← Older revision		Revision as of 04:18, 31 October 2025
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	\|Max no. consecutive dry days (per year)		\|Max no. consecutive dry days (per year)
	\|128.9		\|128.9
	\|128.~~30000000000001~~		\|128.3
	\|124.3		\|124.3
	\|130		\|130
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	\|3.8		\|3.8
	\|2.4		\|2.4
	\|4.~~5999999999999996~~		\|4.6
	\|}		\|}

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	\|Wildfire		\|Wildfire
	\|30		\|30
	\|2.~~5499999999999998~~		\|2.55
	\|30		\|30
	\|2.41		\|2.41