Spatiotemporal variations in length-weight relationship, growth pattern and condition factor of Periophthalmus variabilis Eggert, 1935 in Vietnamese Mekong Delta

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Aquatic Biology

Introduction

The length-weight relationship (LWR) plays an essential role in both evaluating the growth and biomass of a fish population (Khaironizam & Norma-Rashid, 2002; Mahmood et al., 2012; Jin et al., 2015; Dinh, 2016a; Lam & Dinh, 2021) and in assessing fishery management (Froese, 1998; Froese & Pauly, 2000; Gonzalez Acosta, De La Cruz Agüero & De La Cruz Agüero, 2004; Jin et al., 2015; Phan et al., 2021). In addition, the growth pattern and the CF play a vital role in understanding the ecological adaptations of fish (Abdoli et al., 2009; Dinh et al., 2016). The growth pattern and the CF of some fish, including gobies, are affected by sexual, intraspecific and spatiotemporal variables (Froese, 2006; Abdoli et al., 2009; Lam & Dinh, 2021; Phan et al., 2021; Truong et al., 2021). However, this data is limited for mudskippers, one of the gobiid fish groups in the Vietnamese Mekong Delta (VMD).

The mudflats and mangroves are habitats for a number of animal species including fish (Sanders et al., 2010; Sasmito et al., 2020). The mudskipper is a unique fish group that lives mainly in these habitats (Murdy, 1989) and can obtain oxygen directly from the air using their skin and gills (Jaafar, Perrig & Ming Chou, 2009). Periophthalmus is one of the largest genera of mudskippers with 19 described species found throughout the world (Murdy & Jaafar, 2017). Periophthalmus of the VMD is comprised of three species: P. chrysospilos, P. gracilis and P. variabilis (Tran et al., 2013). Of these three species, P. variabilis is found quite frequently in mudflat and mangrove regions (Murdy, 1989; Kottelat et al., 1993; Jaafar & Hou, 2012; Tran et al., 2013; Tran et al., 2020; Tran & Dinh, 2021; Tran et al., 2021a) and can move flexibly in and out of the water to catch prey (Wicaksono et al., 2020). In the VMD, our observations show that the number of individual P. variabilis has decreased over time. However, there is no data on its biology and ecology. This study was conducted to document fish LWR, growth pattern and CF to further understand the ecological adaptations of the P. variabilis population.

Materials and Methods

Study site and fish analysis

The present research was carried out in four locations along the estuarine and coastal regions in the VMD, including Duyen Hai–Tra Vinh (DHTV, 9°40′29.5″N 106°34′49.5″E); Tran De–Soc Trang (TDST, 9°26′19.7″N 105°10′48.1″E); Dong Hai–Bac lieu (DHBL, 9°05′50.5″N 105°29′54.7″E) and Dam Doi–Ca Mau (DDCM, 8°58′10.4″N 105°22′58.9″E) (Fig. 1). There are two seasons at these sites: the dry season from January to May and the wet season from June to December (Le et al., 2006). The dominant plants in DHTV, TDST and DHBL are Sonneratia caseolaris, Avicennia marina and Bruguiera gymnorrhiza, respectively. In DDCM, A. marna and B. gymnorrhiza are equally dominant (Dinh et al., 2021a). The pH ranged from 7.6–8.0, and the salinity varied widely from 12.3 to 23.5%. The pH varied with the site but not with the season, whereas the salinity varied with the season but not the site (Dinh et al., 2021a).

Distribution map of sampling points.

Figure 1: Distribution map of sampling points.

•: Sampling site; 1: Duyen Hai–Tra Vinh; 2:Tran De–Soc Trang; 3: Dong Hai–Bac Lieu; 4: Dam Doi–Ca Mau.

Fish samples were collected monthly by hand for 4-hours at a time in an area of 120 m2 (6-m width × 20-m length) from April 2020 to March 2021. Fish specimens were easily distinguished from congeners using their external features (Murdy & Jaafar, 2017). Periophthalmus variabilis are covered by many irregular blackish dots, whereas P. chrysospilos and P. gracilis are covered by small orange spots and are greyish brown with several irregular narrow white bars, respectively. The roughly triangular first dorsal fin is found on P. variabilis and P. chrysospilos, but not on P. gracilis. Filamentous spines are found in the first dorsal fin of P. chrysospilos but are not found in P. variabilis. MS222 was used to anaesthetize fish specimens before being preserved in a 5% formalin buffer and shipped to the laboratory. In the laboratory, fish sex was differentiated using genital papilla, e.g., a triangle shape in males and an oval shape in females. Fish total length (TL) was measured to the nearest 0.1 cm using a ruler, and fish weight (W) was recorded to the nearest 0.01 g using an electric scale.

Data analysis

The LWR was determined using the formula W = a ×TLb (W: fish weight, a: intercept parameter, TL: fish total length, and b: slope parameter) (Ricker, 1973). The condition factor (CF) was calculated as suggested by Le Cren (1951) using the formula CF = W/(a ×TLb).

The quality of LWR s was determined by using the determination coefficient (r2) (Metin et al., 2011). The t-test was performed to verify if the b value obtained from the LWR s was close to a cubic value. Species displayed positive allometry (b > 3), negative allometry (b < 3) and isometry (b =3) (Martin, 1949). The t-test was applied to confirm whether the CF varied by sex, size and season, while one-way ANOVA was used to assess any variations in th CF between months and sites (Mahmood et al., 2012). The t-test was used to verify if the CF was significantly different from the threshold of 1. A General Linear Model was used to confirm if the interactions of sex × season, sex × site and season × site affected the CF (Dinh, 2016a). The length at first maturity (Lm) was used to divide fish into the immature group if TL < Lm and into the mature group if TLLm (e.g., Lm values of females and males were 5.0 cm and 5.7 cm in DHTV; 4.6 cm and 5.8 cm in TDST; 4.9 cm and 5.2 cm in DHBL; and 6.2 cm and 5.9 cm in DDCM, unpublished data). SPSS v.21 was used for data analysis and all tests were set at p < 0.05. The Benjamini–Hochberg procedure was used to decrease the Type I error of all tests (Benjamini & Hochberg, 1995; McDonald, 2014).

Results

Length-weight relationship and growth pattern

A total of 495 individuals (TL: 3.7–8.5 cm; W: 0.31–7.09 g) were collected from the four sites, as shown in Table 1. The fish weight of males and females in different sizes, seasons, months and sites could be estimated from fish length due to high determination values (r2 = 0.70–0.97, Table 2). The LWR of P. variabilis (female, male and both sexes) was presented in Table 2 as W = aTLb. As the slope parameters (b) obtained from the LWR of males (3.123 ± 0.068, n = 236) and females (3.014 ± 0.064, n =259) were not significantly different from the threshold of 3 (dfmale = 231, tmale = 1.81, pmale = 0.07; dffemale =257, tfemale = 0.22, pfemale = 0.83, Table 2), both males and females displayed an isometric growth pattern. Similarly, the growth pattern of the fish was not affected by its developmental stages since the immature and mature fish both exhibited isometry with b values (2.964 ± 0.071, n = 404) close to 3 (dfimmature =89, timmature = 1.40, pimmature = 0.17; dfmature = 402, tmature = 0.51, pmature = 0.61, Table 2). In contrast, the mudskipper displayed isometry in the wet season as b (3.058 ± 0.061, n = 283) was ≈3 (df = 281, t = 0.95, p = 0.34) but had positive allometry in the dry season since b (3.138 ± 0.065, n =212) was >3 (df = 210, t = 2.21, p = 0.03). In the northern region of the Hau river mouth, P. variabilis exhibited isometry since the b value was ≈3 (bDHTV = 3.007 ± 0.061, nDHTV = 194, dfDHTV = 192, tDHTV = 0.12, pDHTV = 0.91; bTDST = 2.850 ± 0.103, nTDST =119, dfTDST = 117, tTDST = −1.46, pTDST = 0.15, Table 2), but had positive allometry in the southern region because b was > 3 (bDHBL = 3.370 ± 0.114, nDHBL =89, dfDHBL = 87, tDHBL = 3.25, pDHBL< 0.001; bDDCM = 3.232 ± 0.101, nDDCM = 93, dfDDCM = 91, tDDCM = 2.30, pDDCM = 0.02, Table 2). The species displayed isometry in April and again from August through December as the b value (2.668 ± 0.184 - 3.001 ± 0.105) was close to 3 (t-test, p > 0.05 for all cases, Table 3), but displayed positive allometry for the remaining months since the b value (3.215 ± 0.086–3.771 ± 0.325) was significantly higher than 3 (p < 0.05 for all cases, Table 3). Overall, the Dusky-gilled mudskipper displayed positive allometry as the b value (3.094 ± 0.045) was >3 (n = 495, df = 493, t = 2.09, p = 0.04).

Table 1:
Number of samples by sex, site and month.
Months Duyen Hai–Tra Vinh Tran De–Soc Trang Dong Hai–Bac Lieu Dam Doi–Ca Mau
Male Female Male Female Male Female Male Female
Apr-20 12 6 4 5 1 4 1 2
May-20 6 8 5 3 5 1 2 3
Jun-20 12 15 5 5 4 1 6 1
Jul-20 9 5 4 4 6 3 1 5
Aug-20 6 6 6 8 5 5 2 4
Sep-20 6 8 3 6 4 3 5 6
Oct-20 4 9 6 6 2 4 5 3
Nov-20 6 6 5 3 3 4 2 6
Dec-20 8 3 1 10 4 3 8 3
Jan-21 4 22 3 7 3 6 3 8
Feb-21 8 7 4 6 8 2 3 6
Mar-21 9 9 5 5 5 3 6 2
Total 90 104 51 68 50 39 44 49
DOI: 10.7717/peerj.12798/table-1
Table 2:
Variations of growth pattern of P. variabilis by sex, season, size and site (TL, total length; W, body weight; n, number of individuals, b, slope parameter; a, intercept parameter; r2, determination parameter; df, freedom degree).
Fish groups TL W n b± SE a± SE r2 t-value df p-value Growth type
Gender Female 3.7–8.5 0.31–7.09 259 3.014 ± 0.064 0.010 ± 0.001 0.90 0.83 257 0.22 Isometry
Male 4.0–7.9 0.44–4.86 236 3.123 ± 0.068 0.008 ± 0.001 0.90 0.07 234 1.81 Isometry
Season Dry 3.7–8.5 0.31–7.09 212 3.138 ± 0.065 0.008 ± 0.001 0.92 0.03 210 2.12 Positive allometry
Wet 3.8–8.3 0.41–6.79 283 3.058 ± 0.061 0.009 ± 0.001 0.90 0.34 281 0.95 Isometry
Fish size Immatury 3.7–5.7 0.31–2.68 91 3.327 ± 0.234 0.006 ± 0.002 0.70 0.17 89 1.40 Isometry
Matury 5.2–8.5 1.20–7.09 404 2.964 ± 0.071 0.011 ± 0.001 0.81 0.61 402 −0.51 Isometry
Study site Duyen Hai, Tra Vinh 3.8–7.8 0.41–4.76 194 3.007 ± 0.061 0.010 ± 0.001 0.93 0.91 192 0.12 Isometry
Tran De, Soc Trang 4.1–7.9 0.44–4.86 119 2.850 ± 0.103 0.013 ± 0.003 0.87 0.15 117 −1.46 Isometry
Dong Hai, Bac Lieu 3.7–7.5 0.31–4.86 89 3.370 ± 0.114 0.005 ± 0.001 0.91 0.00 87 3.25 Positive allometry
Dam Doi, Ca Mau 7.1–8.5 0.78–7.09 93 3.232 ± 0.101 0.006 ± 0.001 0.92 0.02 91 2.30 Positive allometry
Total 3.7–8.5 0.31–7.09 495 3.094 ± 0.045 0.008 ± 0.001 0.91 2.09 493 0.04 Positive allometry
DOI: 10.7717/peerj.12798/table-2
Table 3:
Variations of growth pattern of P. variabilis by months (TL, total length; W, body weight; n, number of individuals; b, slope parameter; a, intercept parameter; r2, determination parameter; df, freedom degree).
Months TL W n b± SE a± SE r2 t-value p df Growth type
Apr-20 5.6-7.3 1.00-4.66 35 3.588 ± 0.299 0.003 ± 0.002 0.81 2.57 0.01 33 Positive allometry
May-20 5.6-7.3 1.00-4.86 33 3.771 ± 0.325 0.002 ± 0.001 0.81 2.37 0.02 31 Positive allometry
Jun-20 3.9-7.7 0.44-4.76 49 3.390 ± 0.091 0.005 ± 0.001 0.97 4.29 0.00 47 Positive allometry
Jul-20 3.8-7.7 0.41-4.86 37 3.354 ± 0.143 0.005 ± 0.001 0.94 2.48 0.02 35 Positive allometry
Aug-20 4.8-8.3 1.30-6.89 42 2.887 ± 0.198 0.013 ± 0.005 0.84 −0.57 0.57 40 Isometry
Sep-20 4.5-7.8 1.02-4.40 41 2.767 ± 0.234 0.015 ± 0.006 0.78 −1.00 0.33 39 Isometry
Oct-20 4.3-7.8 0.82-4.71 39 2.668 ± 0.184 0.018 ± 0.006 0.85 −1.80 0.08 37 Isometry
Nov-20 4.7-8.2 1.22-6.79 35 2.772 ± 0.210 0.016 ± 0.006 0.84 −1.09 0.29 33 Isometry
Dec-20 4.10-7.7 0.62-4.41 40 3.001 ± 0.105 0.009 ± 0.002 0.96 0.01 0.99 38 Isometry
Jan-21 4.1-8.5 0.50-7.09 56 3.215 ± 0.086 0.006 ± 0.001 0.96 2.50 0.02 54 Positive allometry
Feb-21 3.7-7.9 0.31-4.61 44 3.418 ± 0.086 0.004 ± 0.001 0.97 4.86 0.00 42 Positive allometry
Mar-21 3.9-7.3 0.57-4.38 44 3.229 ± 0.090 0.008 ± 0.001 0.97 2.54 0.01 42 Positive allometry
Total 3.7-8.5 0.31-7.09 495 3.094 ± 0.045 0.008 ± 0.001 0.91 2.09 0.04 493 Positive allometry
DOI: 10.7717/peerj.12798/table-3

Condition factor

The CF of P. variabilis varied by site and month but not by sex, size or season. The CF of males (1.04 ± 0.01, n = 236) was not significantly different from that of females (1.06 ± 0.01, n = 259) (t-test, t = −1.05, n = 495, df = 493, p = 0.29, CI95% = (−0.01)–(0.05)). The CF of the immature group (1.06 ± 0.03, n = 91) was similar to that of the mature group (1.05 ± 0.01, n = 404) (t =  − 0.47, n = 495, df = 493, p = 0.64, CI95% = (−0.05)–(0.08)). The CF in the dry season (1.06 ± 0.01, n = 212) was not significantly higher than in the wet season (1.05 ± 0.01, n = 283) (t = −0.79, n = 495, df = 493, p = 0.43, CI95% = (−0.02)–(0.04)). However, the CF in the DDCM was significantly lower in general than the remaining sites (One-way ANOVA, n = 495, F2,3 = 3.82, p = 0.01, Tukey Post Hoc comparison analysis) (Fig. 2). The CF all the sites in general also fluctuated from 0.93 ± 0.02 to 1.21 ± 0.02 (n = 495, df = 493, F2,11 = 7.69, p < 0.001) (Fig. 3) depending on the month. The CF of this species also varied by sex × site (General Linear Model, n =495, n = 495, F2,3 = 4.67, p = 0.003, Fig. 4), but not by sex × season (F2,1 = 1.30, p = 0.26, Fig. 5), season × site (n = 495, F2,3 = 0.41, p = 6.19, Fig. 6) or sex × season × site (n = 495, df = 1, F2,3 = 1.40, p = 0.24). Overall, the CF value of the mudskipper (1.05 ± 0.02, n = 495) was significantly higher than an ideal threshold value of 1 (t = 6.43, n = 495, df = 494, p < 0.001, CI95% = 0.04–0.07).

Variations of condition factor of P. variabilis by site.

Figure 2: Variations of condition factor of P. variabilis by site.

DHTV, Duyen Hai–TraVinh; TDST, Tran De–Soc Trang; DHBL, Dong Hai–Bac Lieu; DDCM, Dam Doi–Ca Mau; vertical bar is standard error of mean; a and b represent the significant difference; number in each column is number of samples.
Variations of condition factor of P. variabilis by month.

Figure 3: Variations of condition factor of P. variabilis by month.

Letters a and b represent the significant difference; number in each column is number of samples.
Variations of condition factor of P. variabilis by sex and site.

Figure 4: Variations of condition factor of P. variabilis by sex and site.

DHTV, Duyen Hai–TraVinh; TDST, Tran De–Soc Trang; DHBL, Dong Hai–Bac Lieu; DDCM, Dam Doi–Ca Mau; vertical bar is standard error of mean; a and b represent the significant difference; number in parentheses is number of samples.
Variations of condition factor of P. variabilis by sex and season.

Figure 5: Variations of condition factor of P. variabilis by sex and season.

Vertical bar is standard error of mean; number in parentheses is number of samples.
Variations of condition factor of P. variabilis by season and site.

Figure 6: Variations of condition factor of P. variabilis by season and site.

DHTV, Duyen Hai–TraVinh; TDST, Tran De–Soc Trang; DHBL, Dong Hai–Bac Lieu; DDCM: Dam Doi–Ca Mau; vertical bar is standard error of mean; number in parentheses is number of samples.

Discussion

The positive relationship between weight and length was found in male, female, immature and mature P. variabilis due to the high values of the determination coefficients (r2) of the LWRs, suggesting that fish weight could be obtained from fish length regardless of the developmental stage of the fish. As high r2 values were shown in Tables 1 and 2 over a year long study, fish weight and length could be extrapolated using the data from such a large sample size and range. Similarly, a positive relationship between TL and W was found in Periophthalmus spp. living outside of the VMD (Chukwu & Deekae, 2011; Panicker, Katchi & Gore, 2013; Tran, Nguyen & Ha, 2021b). A positive LWR was also found in some other co-occurring gobies, e.g., Pseudapocryptes elongatus (Tran, 2008), Boleophthalmus boddarti (Dinh, 2014b), Glossogobius sparsipapillus (Dinh, 2015), P. serperaster (Dinh et al., 2016), Trypauchen vagina (Dinh, 2016c), Periophthalmodon schlosseri (Dinh, 2016b), Oxyeleotris urophthalmus (Dinh, 2016a), Butis butis (Dinh, 2017b), B. koilomatodon (Lam & Dinh, 2021) and G. giuris (Dinh & Ly, 2014; Phan et al., 2021).

P. variabilis displayed positive allometry (b > 3) and the fish specimens collected were mostly adults, indicating that the fish population in this region was not overfished. By contrast, its congener, e.g., P. barbarus in Nigeria, displayed negative allometry (b = 2.73), indicating that most P. barbarus were caught during the juvenile stage (King & Udo, 1998). Another study on the genus Periophthalmus in Indonesia showed that both P. argentilineatus and P. gracilis had negative allometry (b < 3) (Taniwel & Leiwakabessy, 2020). Negative allometry was also observed in some gobies living in the VMD, e.g., G. aureus (b = 2.71) (Dinh, 2014a; Phan et al., 2021), B. koilomatodon (b = 2.66) (Lam & Dinh, 2021) and G. sparsipapillus (b = 2.68) (Truong et al., 2021). Meanwhile, other gobies living in the VMD exhibited isometric growth, e.g., B. boddarti (Dinh, 2014b), P. serperaster (Dinh et al., 2016), T. vagina (Dinh, 2016c), P. schlosseri (Dinh, 2016b) and G. giuris (Dinh & Ly, 2014; Phan et al., 2021) with a b value of ≈3. Another congener of P. variabilis, e.g., P. modestus found in the Red River Delta in northern Vietnam (VRD), showed positive allometry (b > 3) (Tran, Nguyen & Ha, 2021b). Positive allometry was also found in P. chrysospilos occurring in Malaysia (Abdullah & Zain, 2019) and P. kalolo and P. malaccensis in Indonesia (Taniwel & Leiwakabessy, 2020). Some other fish species living in the VMD, e.g., S. pleurostigma displayed positive allometry as well (b > 3) (Dinh, 2017a). The similarities and differences in the growth pattern of P. variabilis and other gobies obtained from the b value of the LWRs suggest that fish growth type is species specific and regulated by the environment.

The growth pattern of P. variabilis did not change based on sex as both males and females showed isometry, suggesting that the different ovarian and testicular weights did not regulate fish growth type. A similar growth pattern in the two sexes was found in P. barbarus in Nigeria (King & Udo, 1998) but not in P. modestus in the VRD (Tran, Nguyen & Ha, 2021b). The growth pattern of P. variabilis was not impacted by size as evidenced by immature and mature groups both exhibiting isometry. This was also observed in P. barbarus in Nigeria (King & Udo, 1998) but not in P. modestus in the VRD (Tran, Nguyen & Ha, 2021b). Like its congener, P. modestus in the VRD (Tran, Nguyen & Ha, 2021b), the growth pattern of P. variabilis in the dry season was different from in the wet season, indicating that the difference in precipitation between these two seasons affected fish growth type. The various vegetation among the four sites could have an impact on P. variabilis’ growth patterns as well. The impact of environmental conditions on fish growth patterns was also found in P. waltoni in Nigeria (Sarafraz et al., 2012) and P. modestus in the VRD (Tran, Nguyen & Ha, 2021b). Like P. variabilis, some gobies living in and out of the VMD, e.g., P. barbarus (King & Udo, 1998), P. waltoni (Sarafraz et al., 2012), G. giuris (Dinh & Ly, 2014; Phan et al., 2021), B. boddarti (Dinh, 2014b), P. serperaster (Dinh et al., 2016), T. vagina (Dinh, 2016c), P. schlosseri (Dinh, 2016b) and P. modestus (Tran, Nguyen & Ha, 2021b) showed variations in their growth patterns that fluctuated based on the month.

Like B. koilomatodon in the VMD (Lam & Dinh, 2021), the CF of P. variabilis was not affected by its developmental stage as its CF did not change with sex and size. Likewise, the CF of P. variabilis’s congener, P. barbarus, in Nigeria did not indicate changes in the CF based on sex differences (King & Udo, 1998; Chukwu & Deekae, 2011). By contrast, P. modestus, another congener in the VRD, showed a change in its CF due to sex as this value was high in females towards the end of gonadal maturation. Like P. variabilis, the CF of some gobies in the VMD, e.g., Parapocryptes serperaster (Dinh et al., 2016), P. schlosseri (Dinh, 2016b), T. vagina (Dinh, 2016c) and G. giuris (Phan et al., 2021) did not vary with size. P. variabilis could adapt well to environmental conditions as its CF showed a similar pattern in the dry and wet seasons. In contrast, the dry season was preferable for P. modestus in the VRD as its CF value in the dry season was higher than it was in the wet season (Tran, Nguyen & Ha, 2021b). Like P. variabilis, a similar CF value was found between the dry and wet seasons in co-occurring gobiid species such as P. elongatus (Tran, 2008), P. serperaster (Dinh et al., 2016), T. vagina (Dinh, 2016c), G. giuris (Phan et al., 2021) and B. koilomatodon (Lam & Dinh, 2021). The difference in abiotic and biotic factors among sites (Dinh et al., 2021a) could be impacting the CF of P. variabilis as it showed a spatial variation in its CF. This same spatial variation in the CF was also found in the co-occurring goby species B. koilomatodon (Lam & Dinh, 2021) but was not found in the P. modestus species in the VRD (Tran, Nguyen & Ha, 2021b). Although P. variabilis showed spatiotemporal variations in its CF, overall its CF was higher than the threshold of 1 which could indicate that the study site had favourable environmental conditions. Congeners living outside of the VMD e.g., P. barbarus (King & Udo, 1998), P. chrysospilos (Abdullah & Zain, 2019) and P. modestus (Tran, Nguyen & Ha, 2021b) were also well adapted to their habitats as evidenced by higher CFs. This was also observed in some other fish species in the VMD, e.g., P. elongatus (Tran, 2008), P. serperaster (Dinh et al., 2016), T. vagina (Dinh, 2016c), P. schlosseri (Dinh, 2016b), G. aureus (Dinh, 2019), P. chrysospilos (Dinh et al., in press) and G. giuris (Phan et al., 2021).

Conclusions

Due to high determination values fish weight can be estimated using a given fish length. As the slope value obtained from its LWRs was higher than the cubic value, P. variabilis displayed positive allometry. The growth pattern of this species was not affected by sexual and intraspecific factors since male, female, immature and mature fish displayed isometric growth as indicated by a b value ≈3. The CF was not affected by sex, size or season, but did vary by site and month. The CF of this species was higher than 1, showing it adapted well to the environment. These results can play a vital role in the assessment and management of the P. variabilis population in the VMD.

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