Introduction

 

Profitability in livestock farming is adversely affected due to different types of parasitic and vector borne infections (Imran et al. 2018; Rashid et al. 2019; Zafar et al. 2019) and gastrointestinal nematodes (GINs) is one of the major impediments. The most common method for control of GINs is the use of synthetic anthelmintics. The development of resistance in parasites to several families of anthelmintics (Leathwick et al. 2001; Ijaz et al. 2018) has posed a threat in affective chemotherapeutic parasite control. In the last two decades, resistance has developed rapidly throughout the world and increasing incidents of anthelmintic resistance (AR) in Brazil, Argentina, New Zealand, USA, and the UK have been reported (Waghorn et al. 2006; Stafford et al. 2007). This increased prevalence of AR and the issue of drug residues in animal products (Manzoor et al. 2019) have provided a spur for research into ‘alternative/novel’ approaches for control of GINs. The search for novel approaches is not only driven by AR but also by the need for techniques that are feasible for application by resource-poor farmers in non-commercial subsistence farming systems. The utilization of nematophagous fungi (NF), which parasitise nematodes, is one of such alternatives to control the nematode population (Khattak et al. 2018).

Various species of NF have been identified as potential biological control agents to decrease the infection level of GINs in ruminants (Chandrawathani et al. 2004; Waller et al. 2004). These NF belong to all major taxonomic groups but the majority belongs to phylum Ascomycetes (Gams et al. 1998). All NF can be divided into two major groups i.e., predacious and endoparasitic, which are further categorized based on killing or trapping behavior. The predacious fungi construct extensive hyphal structures in their surrounding environment that produce adhesive traps or nets at intervals that trap and kill the nematode. In contrast, the endoparasitic NF produces encysting spores that adhere to and penetrate the egg-shell or conidia that are ingested and grow within the nematode (Basualdo et al. 2000).

Surveys for documentation of NF in the faecal environment have been conducted in various countries of the globe like; Australia (Larsen et al. 1994), Brazil (Saumell et al. 2000), Iran (Ghahfarokhi et al. 2004), Malaysia (Chandrawathani et al. 2002), New Zealand (Skipp et al. 2002) and South Africa (Durand et al. 2005). As far as literature could be ascertained, In Pakistan, no survey to check the prevalence of naturally occurring NF has been conducted. Keeping in view the significance of NF in control of GINs and no availability of data from Pakistan, this study has been planned with objectives to document the species of naturally occurring NF present on pastures in hilly areas. To check the effect of temperature and rainfall on the prevalence of NF, the seasonal variation was also estimated in the current study. This study will provide baseline data on prevalent species of NF and will help in designing a biological control program.

 

Materials and Methods

 

The samples were collected in both the Summer and Winter seasons for three years to record the maximum number of naturally occurring NF in hilly areas. Faecal and soil samples were collected from sheep farms to isolate all naturally occurring NF in the study area. Information obtained was recorded in the form of the frequency of occurrence.

 

Study area

 

Pakistan is a country with varying climatic conditions having four seasons annually i.e., Winter, Spring, Summer, and Autumn. It also has a variety of terrain conditions, mountains, hills, arid lands, and desserts. This study was carried out in the hilly area (District Manshera) to check the difference in the natural occurrence of NF in Summer and Winter Winterseasons for three consecutive years. District Mansehra is mainly a hilly area located in Khyber Pakhtunkhwa, Pakistan. It is located 34.6744° N and 73.3709° E at an altitude of 1,088 meters above sea level. The annual rainfall (1445 mm) is concentrated in the Summer. The climate of the region is rainy in the Summer and dry in Winter. The estimates of temperatures and rain falls during these seasons have been mentioned in Table 1. The average annual temperature in the region falls around 22.5°C.

 

Documentation of nematophagous fungi

 

Collection of faecal samples

 

During each season, a total of 150 random samples were collected (5 g each) from small ruminant livestock farms. Faecal material was acquired directly from the rectum of animals and the ground after wearing gloves. Some soil along faecal deposit area was also collected as naturally occurring NF from the soil surrounding the faecal culture enters the faecal material to predate the larvae. After collection, all the samples were pooled into one big container and mixed to maximize the chances of isolation of NF. All containers were clearly and completely labeled (location, animal, date of collection) and samples were brought to the laboratory at the Department of Parasitology, the University of Agriculture Faisalabad within 12 h after collection.

 

Sample processing

 

In the laboratory, the collected samples were homogenized thoroughly. Out of the homogenized faecal material, 10 samples (2 g each) were crumpled and cultivated on individual Petri dishes comprising 2% water agar with nematode larvae as bait (1000 larvae/Petri dish). Petri dishes were then enclosed and retained at 21–26°C for 3 weeks. Petri dishes were examined underneath the stereomicroscope weekly to check any fungal growth.

 

Isolation and identification of fungi

 

The NF cultured on the Petri plates were then isolated and refined in pure cultures for identification procedure. First, they were shifted to clean water agar plates and L3 from mixed infection of GINs were added to the Petri plates as a source of bait ensuring eminent proliferation. After growth on water agar Petri plates, conidia were then shifted to cornmeal (2%) agar plates and net development was encouraged by the addition of L3 of GINs to pure cultures for identification. The identification was carried out based on morphological features (as the morphology of conidiophores and conidial size in the micro-culture) and trapping structure produced by the fungus on nematode infected culture. This was achieved primarily by following the explanations of Subramanian (1963), Cooke and Godfrey (1964), Cooke and Dickinson (1965), Schenck et al. (1977), van Oorschot (1985), Gams (1988), Liu and Zhang (1994) and Rubner (1996).

 

Results

 

A total of 21 NF belonging to seven different genera were observed. The maximum number of species from genus Arthrobotrys was recorded (n=7) followed by genus Dactylaria (n=5) and Nematoctonus (n=4). Name of individual NF species and their total frequency of occurrence along with different infection structures observed in Summer and Winter seasons have been presented in Table 2 and 3 respectively.

The samples collected (n=150/sampling) in Summer 2013, 2014 and 2015, showed total frequencies of n = 166, n=142 and n= 145, respectively. In Summer 2013 the occurrence of NF with different infection structures Table 1: Avergae temperature and rainfall of district Mansehra, Pakistan

 

Seasons

Summer

Winter

Months

June

July

August

September

December

January

February

Avg. Temperature (°C)

28

26.7

25.3

23.9

10

8

9.8

Min. Temperature (°C)

21.3

21.3

20.4

18

4.2

2.6

4.3

Max. Temperature (°C)

34.8

32.2

30.3

29.9

15.9

13.4

15.3

Precipitation /Rainfall (mm)

91

302

266

113

55

90

127

Adopted from: https://en.climate-data.org (Anonymous, n. d)

 

Table 2: Frequency of occurrence of nematophagous fungi out of collected samples from Jabba farm, Mansehra, KPK, Pakistan in Summer 2013-2015

 

Nematphagus Fungi

Predatory mechanism

Frequency in Summer 2013

Frequency in Summer 2014

Frequency in Summer 2015

Total Frequency

Arthrobortrys robusta

Adhesive nets

21

17

18

56

A. conoides

Adhesive nets

12

9

9

30

A. dactyloides

Constricting rings

4

5

6

15

A. brochopaga

Adhesive spores

5

6

4

15

A. cladodes

Adhesive nets

18

9

22

49

A. oligospora

Adhesive nets

27

19

16

62

A. musiformis

Adhesive nets

8

4

3

15

Cystopage lateralisa

Adhesive mycelia

1

0

1

2

Dactylaria candida

Non-constricting rings

2

1

1

4

D. haptospora

Conidia with adhesive branches

3

0

1

4

D. leptospora

Conidia with adhesive branches

4

6

1

11

D. pyriformis

Conidia with adhesive branches

3

1

2

6

D. sclerohypha

Conidia with adhesive branches

1

2

0

3

D. heterospora

Conidia with adhesive branches

1

0

0

1

D. leptospora

Non-constricting rings

1

1

1

3

Harpsporium anguillulae

Ingested conidia

17

15

12

44

Monacrosporium spp.

Adhesive nets

1

3

1

5

Nematoctonus campylosporus

Conidia with adhesive knobs

3

2

0

5

N. robustus

Adhesive conidia

7

3

6

16

N. haptocladus

Conidia with adhesive knobs

2

0

1

3

N. tylosporus

Conidia with adhesive knobs

1

0

2

3

Total frequency

142

103

107

352

 

Table 3: Frequency of occurrence of nematophagous fungi out of collected samples from Jabba farm, Mansehra, KPK, Pakistan in Winter 2013-2016

 

Nematphagus Fungi

Predatory mechanism

Frequency in Winter 2013-2014

Frequency in Winter 2014-2015

Frequency in Winter 2015-2016

Total Frequency

A. robusta

Adhesive nets

8

7

4

19

A. conoides

Adhesive nets

1

3

6

10

A. dactyloides

Constricting rings

0

1

2

3

A. brochopaga

Adhesive spores

2

0

1

3

A. cladodes

Adhesive nets

1

2

1

4

A. oligospora

Adhesive nets

6

4

8

18

A. musiformis

Adhesive nets

0

1

3

4

Cystopage lateralisa

Adhesive mycelia

0

0

0

0

D. candida

Non-constricting rings

3

1

0

4

D. haptospora

Conidia with adhesive branches

0

0

0

0

D. leptospora

Conidia with adhesive branches

1

0

1

2

D. pyriformis

Conidia with adhesive branches

1

3

4

8

D. sclerohypha

Conidia with adhesive branches

2

1

2

5

D. heterospora

Conidia with adhesive branches

0

0

1

1

D. leptospora

Non-constricting rings

0

1

0

1

H. anguillulae

Ingested conidia

5

2

7

14

Monacrosporium spp

Adhesive nets

1

2

2

5

N. campylosporus

Conidia with adhesive knobs

1

0

0

1

N. robustus

Adhesive conidia

0

0

5

5

N. haptocladus

Conidia with adhesive knobs

0

0

3

3

N. tylosporus

Conidia with adhesive knobs

0

0

4

4

Total frequency

32

28

54

114

 

were; Adhesive nets (n = 87), Constricting rings (n = 4), Adhesive spores (n = 5), Adhesive mycelia (n = 1), Non-constricting rings (n = 3), Conidia with adhesive branches (n = 12), Ingested conidia (n = 17), Conidia with adhesive knobs (n = 6) and Adhesive conidia (n = 7). A. oligospora (n = 27), A. robusta (n = 21), A. cladodes (n = 18), Harpsporium anguillulae (n = 17) were the top four most frequent species. Moreover, second replication of the trial was carried out in Summer of 2014. Out of the total frequency, the occurrence of NF with different infection structures were; adhesive nets (n = 61), constricting rings (n = 5), adhesive spores (n = 6), adhesive mycelia (n = 0), non-constricting rings (n = 2), conidia with adhesive branches (n = 9), ingested conidia (n = 15), conidia with adhesive knobs (n = 2) and adhesive conidia (n = 3), which also shows that NF with adhesive nets were most prevalent and adhesive mycelia were least prevalent as they were absent in this area. Although less frequent than 2013 Arthrobotrys (n = 69) was still the most predominant genus whereas, A. oligospora (n = 19), A. robusta (n = 17), H. anguillulae (n = 15) and Arthrobortrys conoides (n = 9), were the top four most frequent species at Jaba farm, Mansehra in Summer of 2014. In Summer of 2015, the occurrence of NF with different infection structures at this farm were; adhesive nets (n = 69), constricting rings (n = 6), adhesive spores (n = 4), adhesive mycelia (n = 1), non-constricting rings (n = 2), conidia with adhesive branches (n = 4), ingested conidia (n = 12), conidia with adhesive knobs (n = 3) and adhesive conidia (n = 6), which shows that NF with adhesive nets were predominant during all three Summers and adhesive mycelia were least. A. oligospora (n = 16), A. robusta (n = 18), A. cladodes (n = 22) and H. anguillulae (n = 12), were the top four most frequent species in Summer of 2015. Detailed results have been presented in Table 2.

The samples collected from Jabba farm (n=150/sampling) during Winter 201314, 201415 and 201516 showed total frequencies of 50, 40 and 95 (Table 3). Out of the total frequency, the occurrence of NF with different infection structures at this farm were; adhesive nets (n = 17), adhesive spores (n = 2), non-constricting rings (n = 3), conidia with adhesive branches (n = 4), ingested conidia (n = 5), conidia with adhesive knobs (n = 1). The NFs with adhesive nets were most prevalent and constricting rings, adhesive mycelia and adhesive conidia were least prevalent as they were absent at this sampling instance. Arthrobotrys (n = 18) was the most predominant genus whereas, A. robusta (n = 8), A. oligospora (n = 6), H. anguillulae (n = 5) and Dactylaria candida (n = 3), were the top four most frequent species at Jaba farm, Mansehra in Winter of 20132014. In the next trial replication of Winter 20142015, NF with different infection structures were; adhesive nets (n = 19), constricting rings (n = 1), non-constricting rings (n = 2), conidia with adhesive branches (n = 4), and ingested conidia (n = 2). The NFs with adhesive nets were most prevalent and adhesive spores, adhesive mycelia, conidia with adhesive knobs and adhesive conidia were absent in this area sampling. Arthrobotrys (n = 18) was the most predominant genus whereas, A. oligospora (n = 4), A. robusta (n = 7), Dactylaria pyriformis (n = 3) and Arthrobortrys conoides (n = 3), were the top four most frequent species out of all. The frequency of occurrence of NF with different infection structures in Winter 201516 were; adhesive nets (n = 24), constricting rings (n = 2), adhesive spores (n = 1), conidia with adhesive branches (n = 8), ingested conidia (n = 7), conidia with adhesive knobs (n = 7) and adhesive conidia (n = 5). NF with adhesive nets was most prevalent and adhesive mycelia, non-constricting rings were not observed in this area. Arthrobotrys (n = 25) was the most predominant genus out of all, whereas, A. oligospora (n = 8), H. anguillulae (n = 7), Arthrobortrys conoides (n = 6) and Nematoctonus robustus (n = 5), were the most frequently observed species.

 

Discussion

 

Nematode trapping fungi are considered to be a useful biological tool against parasitic nematodes in cattle and sheep (Larsen 2000; Flores-Crespo et al. 2001). The Arthrobotrys genus is distributed worldwide and is known for controlling nematodes by its predatory activity (Dalla Pria et al. 1991; Naves and Campos 1991; Nordbring-Hertz et al. 2011). The NFs belonging to this genus utilizes two different carbon sources, one in organic matter as a saprophyte and the other from the predatory activity against nematodes, which makes it adaptable to different habitats (Wachira et al. 2009). This ability of fungus produces a very little impact on the environment when used as a biological control agent on livestock farms.). In vitro testing of H. anguillulae on faecal cultures and agar media has shown that these fungi are capable of reducing the number of free-living larval stages significantly (Nansen et al. 1988; Waller and Faedo 1993; Mendoza-de Gives and Vazquez-Prats 1994; Mendoza-de Gives et al. 1992, 1994). Charles et al. (1996) also evaluated the efficacy of H. anguillulae in Brazil. He conducted an invitro assay to estimate its efficacy in which he targeted H. contortus and percetage reduction of 99.5% was observed at a dose rate of 300,000 conidia per gram of faeces. Abovementioned and various other studies throughout the world showed significant effect of nematophagous fungi against gastro intestinal nematodes making it a considerable candidate for developmental strategies for control of nematodes.

In this present study, various species of NFs were locally isolated in Mansehra and it was found that they were isolated more abundantly in the soil/faeces collected in Summer as compared to Winter, which was influenced by climatic conditions. In a tropical climate, the development of pre-parasitic forms of trichostrongylid nematodes of sheep on pasture occurs in a few days. Thus, the rapid colonization of faeces by NF would be important in the natural control of these parasites.

Overall, the highest frequency of these NF was observed in the Summer season, and a low frequency was observed in the Winter season. This may be because NF propagates more efficiently in hot humid conditions as compared to low temperatures and dry conditions. The optimum temperature recorded for the growth of NF is 25°C (Anamika 2015). It has been reported that the consequent development of adhesive networks around nematodes, was significantly slower at the lower temperatures (510°C) than the higher temperatures (1530°C). The colonization of the nematode by trophic hyphae is affected by temperature. At temperatures below 15°C, it has been observed that the development of tropic hyphae is reduced (Belder and Jensen 1994). The high prevalence of A. oligospora isolated from livestock farms has also been reported (Mahoney and strongman 1994). In accordance with Saumell et al. (2000), who reported the high prevalence of Arthrobotrys species in Brazil, the mean annual temperature of the location chosen for sampling was 18.5°C, which is similar to the annual temperature (20°C) in the present study area. High prevalence of A. oligospora, A. conoides, and A. robusta have also been reported in Iraq and Oman (Muhsin and Kasim 1998).

The ideal temperature range for the growth and development of the majority of the NF has been found between 1530°C (Cooke 1963; Pandey 1973; Grønvold et al. 1985). The temperature of the study falls close to the ideal temperature of fungal growth this could be the reason for a high frequency of NF recorded during the present study. The largest number of isolates was retrieved from faeces at the beginning of the rainy season (during Summer). During this period of the year, the average minimum as well as maximum temperature is increased.Under these conditions, NF became abundant. In the rainy months, the invasion of the faeces by an abundance of free-living nematodes would facilitate the colonization of predatory fungi. When nematodes are infected by NF, they maintain their motility for some time thus facilitating dispersal. The presence of a larger number of isolates of NF in rainy months was also reported in the organic matter of the soil, where sheep pastured. Fungi, which form adhesive nets, were predominant during the dry season. However, A. oligospora, among the predatory fungi, was isolated in every sampling, demonstrating their abundance in the environment and their capacity to colonize faeces and develop in both the wet and dry months. Adhesive net-forming fungi A. oligospora , which were the most abundant predatory species in the dry months, may resist drying out, as was observed by (Gray and Bailey 1985).

 

Conclusion

 

For the treatment of nematode infections in livestock and to prevent the spread of larvae in the environment, these NF may be directly administered to animals. This may provide a strategy for the control of further environmental contamination by the nematode larvae. In vitro studies are pivotal to select effective NF before their application in the field. However, in vitro studies may give an overestimate about the efficacy of NF; as in these trials, the nematodes cannot escape and reproduce as they have in the natural environment. Also, they have limited physical space and less evaluation time. So, in vivo studies may also be conducted for the proper estimation of the predatory activity.

 

Acknowledgments

 

Authors are highly thankful to Prof. Dr. Sajjad-ur-Rehman, Director Institute of Microbiology, University of Agriculture Faisalabad for his help in the cultivation and identification of fungi. We also acknowledge the support of the staff of the Experimental Research Station, Jabba.

 

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