Toxicity Episodes of Mimosa Invisa in Cattle and Buffaloes

Shridhar, N. B.

doi:10.22506/ti/2017/v24/i2/162430

Cited by 4 publications

(5 citation statements)

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“…In our results IM induced histological alterations in liver tissue. these result were in agreement with the results obtained by Duzguner and Erdogan [18] and Toor et al [51]. Histological changes induced in liver by IM were ameliorated in rats which treated with S.honey, this refers to the antioxidant properties of S.honey.…”

Section: Discussionsupporting

confidence: 93%

The protective effect of Sider honey and Zinc on imidacloprid induced hepatorenal and hematological toxicity in rats

Al-Awar¹,

Gumaih²,

Al-Ameri³

et al. 2018

Journal of Natural Sciences, Life and Applied Sciences

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هدفت الدراسة الحالية إلى تقييم قدرة مضادات الأكسدة; عسل السدر والزنك (منفصلة ومجتمعة) لمدة 30 يوماً في التخفيف من الأضرار الكبدية والكلوية والدموية المحدثة بالمبيد الحشري الإيميداكلوبريد في الجرذان. معاملة الجرذان بالإيميداكلوبرايد عن طريق الفم أدت إلى زيادة معنوية في نشاط إنزيمات الكبد (AST & ALT) ومؤشرات وظائف الكلى (اليوريا, حمض اليوريك والكرياتينيين), ومستويات الدهون (الكوليسترول الكلي, الدهون الثلاثية و الدهون منخفضة الكثافة), صاحب ذلك انخفاض معنوي في مستوى البروتين الكلي والألبيومين والدهون مرتفعة الكثافة, بالإضافة إلى ذلك انخفاض معنوي في عدد كريات الدم الحمراء والصفائح الدموية ومستوى الهيموجلوبين مع زيادة معنوية في عدد كريات الدم البيضاء, وكشفت المقاطع النسيجية للكبد والكلى أضراراً كبيرةً بعد معاملتها بالإيميداكلوبريد. من ناحية أخرى, أدى النظام الغذائي المكمل لكلٍ من عسل السدر والزنك بجرعة منخفضة (منفصلة ومجتمعة) عند استخدامهما كمرافق وقائي إلى تحسين الآثار الضارة للإيميداكلوبريد على كل المؤشرات الكيموحيوية والنسيجية المدروسة, والذي قد يكون عائداً لخصائصها المضادة للأكسدة وقدرتها على كسح الجذور الحرة, في حين أن المعاملة بالزنك بجرعة عالية لوحده أو في تركيبة مع عسل السدر سبب آثاراً سلبية على الكبد, وبالتالي هنالك حاجة إلى المزيد من الدراسات لتحديد الجرعات المناسبة من العسل والزنك كمضادات للأكسدة بدون آثار جانبية.

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Section: Discussionsupporting

confidence: 93%

The protective effect of Sider honey and Zinc on imidacloprid induced hepatorenal and hematological toxicity in rats

Al-Awar¹,

Gumaih²,

Al-Ameri³

et al. 2018

Journal of Natural Sciences, Life and Applied Sciences

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“…In our study respondents said that they had seen cattle and goats eat the mimosa flowers and leaves with no ill effects, with the exception of a few who noticed that livestock developed diarrhoea after consumption. This is contrary to other studies, which found mimosa to be toxic to livestock (Alex et al 1991;Gibson & Waring 1994;Li et al 1996;Rajan et al 1986;Shridhar 2017;Tungtrakanpoung & Rhienpanish 1992;Waterhouse & Norris 1987). Shridhar (2017) reported on 16 cows and ten buffaloes that had accidentally consumed mimosa leaves.…”

Section: Impacts Of Mimosa Diplotrichacontrasting

confidence: 66%

“…This is contrary to other studies, which found mimosa to be toxic to livestock (Alex et al 1991;Gibson & Waring 1994;Li et al 1996;Rajan et al 1986;Shridhar 2017;Tungtrakanpoung & Rhienpanish 1992;Waterhouse & Norris 1987). Shridhar (2017) reported on 16 cows and ten buffaloes that had accidentally consumed mimosa leaves. Of the 26 animals, 22 exhibited perineal oedema and died within 14 days of consumption (Shridhar 2017).…”

Section: Impacts Of Mimosa Diplotrichacontrasting

confidence: 66%

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Distribution of Mimosa diplotricha in eastern and southern Africa and its socioecological impacts in northern Malawi

Witt

Chimphepo²,

Beale

et al. 2020

Bothalia ABC

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Background: Mimosa diplotricha is an emerging or established weed in many parts of the world, including many countries in Africa, where it is impacting on biodiversity, crop and pasture production, and driving socio-ecological change. Objectives: To establish the current distribution of M. diplotricha in eastern and southern Africa and its impacts on livelihoods in northern Malawi. Methods: Records on current distribution were collected from roadside surveys, literature reviews and herbarium data. Household surveys were conducted in the Karonga District, Malawi, to understand its impacts on local livelihoods. Results: Mimosa diplotricha is abundant in western Ethiopia, southern Tanzania, and northern and southeastern Malawi with isolated populations in western Rwanda, Burundi, Mozambique, and on the northern shores of Lake Victoria in Uganda. Most respondents said that M. diplotricha invasions were reducing the amount of grass and shrubs in rangelands, with over half saying it reduced crop yields. This invasive plant is also reducing the availability of medicinal plants and other natural resources. Conclusions: Mimosa diplotricha has the potential to significantly expand its range in eastern Africa, and parts of southern Africa, and as such there is an urgent need to develop and implement an integrated management strategy, including biological control, to reduce the negative effects of this invasive plant on local livelihoods.

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“…Mimosa diplotricha is known to have significant negative impacts on livelihood through reduced forage production in range lands, interfering human movements, reduced abundance of medicinal plants, and crop yield loss (Witt et al., 2020 ). Consumption of this weed by cattle may lead to their death because of nephrotoxicity (Sankaran & Suresh, 2013 ; Shridhar & Kumar, 2014 ). Two varieties of M. diplotricha have been reported in Nepal (Sharma et al., 2020 ).…”

Section: Methodsmentioning

confidence: 99%

Germination patterns and seedling growth of congeneric native and invasive Mimosa species: Implications for risk assessment

Kharel,

Dangol,

Shrestha

et al. 2024

Ecology and Evolution

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Comparisons of plant traits between native and invasive congeners are useful approaches for identifying characteristics that promote invasiveness. We compared germination patterns and seedling growth of locally sympatric populations of native Mimosa himalayana and two varieties of invasive M. diplotricha (var. diplotricha and var. inermis) growing in southeastern Nepal. Seeds were germinated under a 12‐h photoperiod or complete dark, low (25/15°C day/night) and high (30/20°C) temperatures, different water stress levels (0, −0.1, −0.25, −0.5, −0.75 and −1.0 MPa), and soil depths (0, 2, and 4 cm). Plant height, biomass allocations, and relative growth rate (RGR) of seedlings were measured. Invasive M. diplotricha had higher germination percentage, rate, and shorter germination time compared with the native species. Germination of both congeners declined as water stress increased, but the decline was more pronounced in native species. Seedling emergence declined with increasing depth in all taxa. The seedlings of invasive species were taller with higher leaf number and allocated greater proportion of biomass to shoot, whereas the native congener allocated greater biomass to root. The RGR was nearly twice as high in invasive species as it was in the native congener. Seedling height and number of leaves were always higher in invasive than in native species, and the native–invasive differences increased over time. Better germination and higher growth performance of invasive species than the congeneric native one suggests that seed germination and seedling growth can be useful traits for the prediction of species' invasiveness in their introduced range during risk assessment process.

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Toxicity Episodes of Mimosa Invisa in Cattle and Buffaloes

Cited by 4 publications

References 0 publications

The protective effect of Sider honey and Zinc on imidacloprid induced hepatorenal and hematological toxicity in rats

The protective effect of Sider honey and Zinc on imidacloprid induced hepatorenal and hematological toxicity in rats

Distribution of Mimosa diplotricha in eastern and southern Africa and its socioecological impacts in northern Malawi

Germination patterns and seedling growth of congeneric native and invasive Mimosa species: Implications for risk assessment

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