American Journal of Plant Sciences
Vol.10 No.01(2019), Article ID:90200,12 pages
10.4236/ajps.2019.101018

Impact of Climate Change on Epidemiology of Various Pests of Wheat Crop in Punjab Pakistan

Israr Arshad1, Amer Rasul1, Syed Ismat Hussain1, Hafiz Muhammad Usman Aslam2,3, Khizar Hayat1*, Malik Najam Ul Hassan1, Sidra Muqeet1*, Amina4, Yasir Umar1, Shabab Nasir5, Anum Tehseen6

1Directorate of Pest Warning & Quality Control of Pesticides, Punjab, Pakistan

2Department of Plant Pathology, University of Agriculture, Faisalabad, Pakistan

3Department of Plant Pathology and Microbiology, Iowa State University, USA

4Horticultural Research Institute, Ayub Agricultural Research Institute (AARI), Faisalabad, Pakistan

5Department of Zoology, Government College University Faisalabad, Faisalabad, Pakistan

6Institute of Agriculture & Resource Economics, University of Agriculture, Faisalabad, Pakistan

Copyright © 2019 by author(s) and Scientific Research Publishing Inc.

This work is licensed under the Creative Commons Attribution International License (CC BY 4.0).

http://creativecommons.org/licenses/by/4.0/

Received: December 23, 2018; Accepted: January 22, 2019; Published: January 25, 2019

ABSTRACT

Wheat [Triticum aestivum L. (Poaceae)] is the staple diet of people in Pakistan. It is attacked by many types of pests. Therefore the purpose of this study was to assess the impact of climate change on the ecology and epidemiology of various wheat pests in Punjab, Pakistan. Results indicate that maximum weeds hot spots 242 (5.98%) Phalaris minor, 45 (1.18%) wild oat and 203 (5.01%) broad leaf weeds were noted in 2015. Aphid 31 (0.86%) hot spots were recorded in 2016 while maximum army worm 13 (0.26%) hot spots were noted in 2017. Maximum 70 (1.73%) spots of yellow rust and 85 (2.10%) hot spots of brown rust were observed during 2015 while 84 (4.16%) spots of loose smut were observed during 2017. ANOVA shows that years have no significant difference (P > 0.05) but weeks have significant effect on occurrence of these pest incidences except brown rust. But regression ANOVA was significant (P ≤ 0.05) and regression models equations have been developed on the bases of recorded data. Pest incidence was taken as dependent variable Y and weather factors i.e. minimum temperature as X1, maximum temperature as X2, relative humidity as X3 and rain fall as X4 were taken as independent variables. This study will help in recommendations for moving forward aiming at integration of biology of rust and smut diseases of wheat with changing climate for development of resistant varieties for resilient and durable management of these pathogens.

Keywords:

Climate Change, Wheat, Weeds, Insect Pest, Disease Ecology

1. Introduction

Wheat [Triticum aestivum L. (Poaceae)] is a crop of paramount importance and one of the major staple foods of people in Pakistan [1] . More than 30 wheat varieties are grown in Pakistan. About 50 diseases have been reported on wheat crop. Globally, all crop production practices are being highly challenged by biotic and abiotic stresses. Biotic stresses especially weeds, insect pests and diseases cause devastating damage in terms of yield and quality. On average pests cause 20% - 37% yield losses worldwide which translating to approximately 70$ billion annually [2] . In agro-ecosystems, herbivore insects are abundant and likely to colonize within same population and disperse from one crop field to another depending on the availability of plant tissues and feeding behavior of insects. Quantitative feeding style of the herbivore insect on specific crop results in significant damage to the crop during the entire life cycle, which is believed specific insect as pest of that particular crop. Single pest may attack multiple crops within single growing season that make crop rotation and pest management more challenged. Wheat producing areas encounter with either sucking and piercing pests or plant tissue feeding pests. Regional pests also observed in wheat growing areas as major damaging-pests worldwide. The breeding strategy against these insects/pests heavily relies on the inheritance of resistance mechanism in the crops under consideration. Climatic conditions and temperature in particular, plays a significant role in population dynamics of the aphids. A warmer temperature can potentially accelerate the aphid’s growth both in terms of number and size, yet, the extreme temperatures can possibly limit the survival and spread of the aphids. Yellow rust (Puccinia striiformis), brown rust (Puccinia recondita) and loose smut (Ustilago tritici) are the most frequently occurring diseases of wheat crop across the wheat cultivating areas in Pakistan which greatly affect the production of wheat and may lead to significant yield losses every year [3] [4] [5] . Although, many diseases of wheat are considered of little values but severe attack of black/stem rust was recorded on wheat crop in 1906-08 at Mirpurkhas, Sindh, Pakistan. Long ago, yellow/stripe and brown/leaf rust were also seen in 1978 all over the wheat producing areas of Pakistan [6] . Yellow stripe rust, caused by a fungus Puccinia striiformis tritici, is one of the devastating diseases of wheat in all wheat growing areas of the World [7] . The severity and frequency of yellow stripe rust epidemics have increased rapidly since 2000 [8] . The prevailing climatic predictions indicate that weather conditions like mild atmospheric temperature is becoming more favorable for rusts than previously occurring and leading to more frequent destructive epidemics of medium to high intensity in longer term [9] . Historically wheat stem rust (Puccinia graminis tritici) has been considered economically more dangerous disease of wheat but the increased geographic extent and yield losses caused by stripe rust indicate that stripe rust is more overwhelming worldwide [10] [11] . Climate change may affect agricultural system in a variety of ways by changing in pests and diseases incidences and intensities in addition to many other abnormalities which may damage foods for their nutritional quality [12] . Although, it is limited but the studies showed that climate change may change the developmental phases of pathogens affecting the crops. The climate change may disturb the pathogens dispersal, which can shift the geographical distribution of hosts and pathogens, resulting in more crop losses [13] . Although, novel pathogens originally occur in limited geographic areas, they can quickly emerge in new regions if they find a production system with vulnerable hosts and favorable environmental conditions. Many pathogens have been introduced long ago in widespread food crops and are now widely distributed geographically [14] . Though the introductions may have occurred centuries ago, the development of such ubiquitous pathogens remains an important cause of concern over the risk of recurrence caused by the adventitious spread of new multi-virulence breeds [15] or new highly aggressive strains [16] . A deep understanding of the origin, distribution and diversity of inoculums reservoirs and past and new pathways of migration of these pathogens is critical to understand current epidemics, developing risk assessment models and mitigating the potential adverse effects of disease [17] [18] . This is especially true for pathogens capable of long-distance migration, where any newly beneficial mutant (increased virulence, aggressiveness or resistance to fungal surfactants) can spread across large geographical areas [19] . Now, brown and yellow rust is a prime example of a worldwide pathogen [20] that has significant negative effects on wheat production due to emergence and invasion of new breeds [10] [16] [21] [22] [23] . Despite the ability to migrate long-haul, yellow rust's worldwide expansion is relatively new, with most emerging site emergencies only reported in the last two decades [9] . Therefore, the purpose of this study was to assess the impact of climate change on the ecology and epidemiology of rust smut and other wheat diseases in Pakistan. This will be followed by recommendations for moving forward aiming at integration of biology of different pests of wheat under changing climate for development of resistant varieties for resilient and durable management of these pest complexes.

2. Materials and Methods

Surveys of central mix crop zone of Punjab (Pakistan), including four districts viz. Faisalabad, TT Singh, Jhang and Chiniot (Figure 1) were conducted in 2015, 2016 and 2017 to determine the pest incidences of wheat crop. Pest scouting for narrow and broad leaf weeds was done by Quadrate method by placing I m2 quadrate at four places randomly and counting the weeds population in the field. Hot spot of P. minor and wild oat was 2 weeds per I m2 each. While aphid and army worm population was noted by selecting 20 tillers randomly and counting the insect’s population on upper, middle and lower leaf in sequence. Hot spot of aphid was 15 aphids/spike, while army worm on appearance. Diseases incidence was recorded as described by [3] . For rust and smut scale 0 - 9 was used [24] . Hot spots of diseases were also considered just on appearance. Surveys were conducted randomly in farmers’ fields at Tehsil level by pest scouting eight to

Figure 1. Study area.

ten spots daily, 4 days a week from 1st January to 15th of April of each three years 2015-17. For accurate identification, infected wheat samples were brought to Plant Pathological Research Institute PPRI located in Ayyub Agricultural Research Institute (AARI), Faisalabad.

Statistical Analysis

Factorial ANOVA without replication was performed to evaluate the differences among different pest incidences and multiple regression ANOVA were also calculated to correlate various pests incidence with climatic conditions at 5% significance levels using SPSS Ver.15.

3. Results

Total 4046, 3603 and 4892 spots were checked during 2015, 2016 and 2017 respectively. Results indicate that maximum weeds hot spots 242 (5.98%) Phalaris minor, 45 (1.18%) wild oat and 203 (5.01%) broad leaf weeds were noted in 2015 (Figure 2). Aphid 31 (0.86%) hot spots were recorded in 2016 while maximum army worm 13 (0.26%) hot spots were noted in 2017 [5] . Week wise hot spots of p. minor, wild oat and broad leaf weeds are shown in Figures 3-5 respectively. Figure 6 shows total spots and% age hot spots of wheat aphid and army worm. Week wise hot spots of aphid and army worm are shown in Figure 7 and Figure 8 respectively. Whereas 1.12% - 1.73% yellow rust, 1.39% - 2.10% brown rust and 2.83% - 4.16% L. smut in three years are shown in Figure 9.

While yellow rust, brown rust and loose smut are shown in Figures 10-12 respectively. Results indicate that maximum p. minor spots were recorded in 3rd week of Jan 2015, whereas w.oat appeared at peak on 4th week of January 2015. Broad leaf weeds reached their climax on 3rd week of January 2017. Aphid hot spot were noted maximum on 1st and 2nd week of March. Army worm appear on 1st week of February 2017. Maximum spots of yellow rust and loose smut were

Figure 2. Total spots and% age hot spots of different weeds.

Figure 3. Week wise hot spots of p. minor.

Figure 4. Week wise hot spots of wild oat.

Figure 5. Week hot spots of broad leaf weeds.

Figure 6. Total spots and % age hot spots of wheat aphid and army worm.

Figure 7. Week wise hot spots of aphid.

Figure 8. Week wise hot spots of army worm.

Figure 9. Total spots, total hot spots and% age hot spots of YR = Yellow rust, BR = Brown rust and LS = Loose smut.

Figure 10. Week wise hot spots of yellow rust.

Figure 11. Week wise hot spots of brown rust.

Figure 12. Week wise hot spots of loose smut.

recorded in 3rd week of March while brown rust appeared on 2nd week of April from 2015-17.

While ANOVA for weeds, insect pests and diseases are shown in Tables 1-3 respectively. ANOVA shows that year have no significant difference (P > 0.05) but week have significant effect on occurrence of pest and disease incidence except brown rust. But regression ANOVA was significant (P ≤ 0.05) and regression equations are given in Table 4. Pest incidence was taken as Y and weather factors i.e. Minimum temperature as X1 maximum temperature as X2 relative humidity as X3 and rain fall as X4. Multiple regression equation were derived using SPSS Ver.15.

Results indicate that maximum 70 (1.73%) spots of yellow rust and 85 (2.10%) hot spots of brown rust were observed during 2015 while 84 (4.16%) of loose smut were observed during 2017.

Table 1. ANOVA for P. minor.

Table 2. ANOVA for aphid and army worm.

Table 3. ANOVA for diseases.

Table 4. Regression models.

Y1 = Hot spots of p. minor; Y2 = Hot spots of wild oat; Y3 = Hot spots of broad leaf; Y4 = Hot spots of aphid; Y5 = Hot spots of Arm Y worm; Y6 = Hot spots of Yellow rust; Y7 = Hot spots of brown rust; Y8 = Hot spots L. Smut.

4. Discussion

Extensive surveys have been conducted to collect weeds, insect pests, diseases and weather data. Multiple regression models have been developed first time in Punjab Pakistan. This study will be helpful for future risk assessment of losses associated with various pests of wheat crop. Integrating the data series and reproduction models can be valuable approach in projection of future climate change on population dynamics of wheat pests. This need to collect long term weather parameters data to create and validate associated “Climate Crop Disease Models” [25] [26] [27] [28] .

In addition to the recently colonized areas, new races are known to emerge periodically through the acquisition of new virulence. The population structure of Yellow rust is therefore likely to be characterized by a complex mixture of reappearances of different genotypes to continuous wheat acreage and rare soil events due to long-distance migration. The recent spread of the pathogen is likely to lead to significant changes in the patterns of population differentiation between geographic regions and possibly erase the signature of previous colonization events.

A recent global population diversity analysis of yellow rust found a strong demographic breakdown within yellow rust, with isolates grouped by geographical origin despite long-haul migration capacity [20] [23] . This pattern is in contrast to the earlier understanding of rust’s global population structure, which considers the potential replacement locally populations from new invasions [19] [22] . Based on survey data monitoring the emergence of strains with newly acquired virulence defeating the recently used Yr (resistance) genes, the population structure of yellow rust has been considered to be due to a continuous replacement of already existing populations by the newly formed races. This process is known as the boom and bust cycle [29] . Such geographic migrations have recently been documented in a global population analysis of yellow rust [20] , but recently scattered genotypes appear to coincide with older populations specific to the main geographical areas, suggesting that migrants displace the local population despite the Capacity not replace recurring remote dispersion. In contrast, invasion of a region by new genotypes in colonial populations would result in a population replacing the original population.

This has been observed in the US, where the yellow rust population after 2000 is dominated by aggressive breeds such as yellow rust S1 or its derivatives originating in the East Africa or Middle East region [30] .

5. Conclusion

Weeds insect pest and diseases are highly affected by weather factors. Therefore studies must be conducted to explore additional factors like crop genotype and soil structure to monitor the occurrence of wheat pests in developing countries like Pakistan.

Acknowledgements

The authors are highly grateful to department of Pest Warning & Quality Control of Pesticides, Punjab, Pakistan for providing competent staff to collect the field data.

Conflicts of Interest

The authors declare no conflicts of interest regarding the publication of this paper.

Cite this paper

Arshad, I., Rasul, A., Hussain, S.I., Aslam, H.M.U., Hayat, K., Ul Hassan, M.N., Muqeet, S., Amina, Umar, Y., Nasir, S. and Tehseen, A. (2019) Impact of Climate Change on Epidemiology of Various Pests of Wheat Crop in Punjab Pakistan. American Journal of Plant Sciences, 10, 236-247. https://doi.org/10.4236/ajps.2019.101018

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