Keywords
Acari, developmental plasticity, maternal effect, phenotypic plasticity, 31
Phytoseiidae, transgenerational phenotypic plasticity 32
33
1 Introduction 34
To cope with environmental variability, organisms have evolved diverse strategies to 35
optimise survival and reproduction (West-Eberhard, 1989). One such strategy is phenotypic 36
plasticity, which is defined as the ability of a single genotype to produce different phenotypes 37
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in response to environmental variation (West-Eberhard, 2003). Phenotypic adjustments can 38
occur during an organism’s development, a process known as developmental plasticity, 39
which often results in irreversible trait changes (Piersma & Drent, 2003; West-Eberhard, 40
2005; Blanckenhorn, 2009; Taborsky, 2017). Developmental plasticity allows individuals to 41
adjust life-history traits such as growth rate, development time, and size at maturity, 42
particularly under suboptimal conditions such as food limitation or temperature stress 43
(Stearns & Koella, 1986; Blanckenhorn, 1999; Bize et al., 2003). This ability is especially 44
important in species with determinate growth, where development ceases upon maturity (Bize 45
et al., 2003). 46
However, plastic responses are not confined to an individual’s own generation 47
(Räsänen & Kruuk, 2007; Bonduriansky & Head, 2007). Increasing evidence shows that 48
parental environmental experiences can shape offspring phenotypes via maternal and/or 49
paternal effects, a form of non-genetic inheritance that is widespread across taxa 50
(Bonduriansky & Day, 2009; Bonduriansky, 2012; Luquet & Tariel, 2016; Kuijper & 51
Johnstone, 2018; Bell & Hellmann, 2019). Through mechanisms such as epigenetic 52
modification, hormonal signalling, or differential provisioning, parents can influence 53
offspring traits including body size, development, stress tolerance, and survival 54
(Bonduriansky & Day, 2009; Bonduriansky, 2012; Luquet & Tariel, 2016; Kuijper & 55
Johnstone, 2018; Bell & Hellmann, 2019; Groothuis et al., 2020). Parental effects can also 56
alter offspring developmental trajectories (Plaistow et al., 2004; Luquet & Tariel, 2016; 57
Groothuis et al., 2020). 58
Among intrinsic parental factors, maternal age has emerged as a key determinant of 59
offspring phenotype (Plaistow et al., 2015; Perez et al., 2017; Bonduriansky et al., 2018; 60
Hernández et al., 2020). The decline in offspring performance with maternal age—known as 61
the Lansing effect or maternal effect senescence—has been found across a wide range of 62
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taxa, from rotifers and insects to birds and mammals (Lansing, 1947; Fox et al., 2003; 63
Bouwhuis et al., 2015; Schroeder et al., 2015; Moorad & Nussey, 2016; Reichert et al., 2020; 64
Krug et al., 2020; Ivimey-Cook et al., 2023). Maternal age effects can manifest as reduced 65
hatching success, lower stress resistance, smaller size, or shortened lifespan in offspring 66
(Halle et al., 2015; Bloch Qazi et al., 2017; Hernández et al., 2020). The adverse influences 67
of advanced maternal age are often context-dependent and shaped by environmental 68
conditions such as diet (Plaistow & Benton, 2009; Gribble et al., 2014; van Daalen et al., 69
2022). 70
Two main theoretical frameworks have been put forward to explain maternal age 71
effects. The senescent parent hypothesis proposes that physiological deterioration reduces 72
gamete quality or maternal provisioning, thereby reducing offspring fitness (Kong et al., 73
2012; Plaistow et al., 2015; Bloch Qazi et al., 2017). For example, maternal age is linked to 74
oxidative damage in Drosophila oocytes (Fredriksson et al., 2012) and reduced nutrient 75
provisioning in eggs of the wasp Eupelmus vuilletti (Muller et al. 2017). Such findings 76
challenge the traditional separation between germline and soma, suggesting that age-related 77
decline can penetrate the Weismann barrier (Monaghan & Metcalfe, 2019). By contrast, 78
adaptive hypotheses predict age-related shifts in reproductive strategy (Goos et al. 2019). 79
Both the asset protection principle and the reproductive restraint hypothesis suggest that older 80
individuals may reduce reproductive effort and increase investment in somatic maintenance 81
(Clark, 1994; Jehan et al., 2021). Conversely, the terminal investment hypothesis suggests 82
increased reproductive effort late in life (Monaghan et al., 2020; Jehan et al., 2021). For 83
instance, young soil mite (Sancassania berlesei) mothers produce more but smaller eggs, 84
whereas older mothers produce fewer but larger ones (Plaistow et al., 2007). 85
Crucially, the strength and direction of maternal age effects often depend on 86
environmental conditions, especially diet (Rollinson & Hutchings, 2013; van Daalen et al., 87
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2022). Diet stress can exacerbate negative effects on offspring (Vijendravarma et al., 2010; 88
Hafer et al., 2011), whereas mild diet restriction (i.e., caloric restriction) may extend maternal 89
lifespan and sometimes even enhance offspring performance (Gribble et al., 2014; Hibshman 90
et al., 2016). Interactions between maternal age and diet are predicted to strongly influence 91
offspring developmental plasticity (van den Heuvel et al., 2016). 92
Despite growing recognition of these interactions, empirical studies remain scarce. To 93
address this, we investigated the combined effects of maternal age and diet on the offspring 94
of a thelytokous predatory mite, Amblyseius herbicolus (Chant) (Acari: Phytoseiidae). This 95
asexual, oviparous species provides a system that eliminates confounding factors such as 96
paternal genetic input and maternal care, enabling a clear focus on physiological and 97
epigenetic maternal effects (Castonguay & Angers, 2012; Verhoeven & Preite, 2014; 98
Groothuis et al., 2020; Vogt, 2021). Although no Lansing effect was previously detected in 99
A. herbicolus when fed ad libitum prey, older females consistently produced smaller eggs, 100
suggesting age-related shifts in provisioning (Zhang et al., 2024). How these shifts influence 101
offspring developmental plasticity remains unclear. 102
Here, we tested two hypotheses: 103
1. Offspring of older mothers exhibit reduced developmental plasticity, expressed as 104
narrower ranges of developmental time and body size at maturity. 105
2. Dietary restriction modulates maternal age effects, strengthening negative age effects 106
under low-resource conditions. 107
By examining the interaction between maternal condition and offspring 108
developmental plasticity, this study provides insights into our understanding of 109
transgenerational effects and their ecological and evolutionary significance, especially in 110
asexually reproducing species. 111
112
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2 Materials and Methods 113
2.1 Study animals and feeding conditions 114
Amblyseius herbicolus is a generalist predatory mite, typically less than 500 µm in body 115
length (McMurtry et al., 2013; Zhang & Zhang, 2021). It has five life stages (egg, larva, 116
protonymph, deutonymph, and adult; FIGURE S1), a developmental period of about 1 week, 117
and a lifespan of about 1 month under laboratory conditions (Liu et al., 2024a). We used a 118
laboratory population of A. herbicolus to examine the influence of maternal age and diet on 119
offspring developmental plasticity. The founding population (>30 adult females) was 120
collected from avocado (Persea americana Mill.) leaves in an orchard in Te Puna, Tauranga, 121
New Zealand. Species identification was confirmed based on morphological characteristics 122
described by Ma et al. (2024). After collection, predatory mites were fed the dried fruit mite 123
Carpoglyphus lactis L. (Acari: Carpoglyphidae), sourced from Bioforce Limited (Karaka, 124
Auckland, New Zealand), for 3 months before the experiment (approximately six 125
generations). Colonies were maintained on water-filled plates (Figure S2A; Zhang & Zhang, 126
2021) within plexiglass cabinets at 25 °C ± 1 °C, 80% ± 5% relative humidity, and a 16:8 h 127
(light:dark) photoperiod. 128
129
2.2 Preparing prey eggs 130
Frozen C. lactis eggs were used as prey. These eggs are suitable food for predatory mites 131
(Liu et al., 2024a). Using non-viable eggs reduced contamination from yeast-based rearing 132
and the need for frequent cell changes. Eggs of C. lactis were collected following Liu et al. 133
(2024b), frozen at -18 °C for about a week, thawed at room temperature for 20 min, and used 134
within 1 month of freezing. 135
136
2.3 Experimental procedures 137
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2.3.1 Maternal generation 138
Approximately 50 A. herbicolus eggs (<16 h old) were transferred to new plates 139
(FIGURE S2A) and reared with ad libitum access to mixed-stage C. lactis. Eggs were 140
collected by placing 1 cm sewing threads in colonies overnight, producing synchronous 141
cohorts. Development to adulthood requires ~10 days, so new threads were placed on days 142
10–15 to collect newly laid eggs (<16 h old). Threads were replaced daily, and collected eggs 143
were used in experiments (FIGURE 1A). 144
145
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146
FIGURE 1. Schematic representation of the experimental design used in this study. A: 147
Experimental setup for examining the effects of maternal age and dietary conditions on the 148
developmental plasticity of Amblyseius herbicolus offspring. Sample sizes (N) are provided 149
for each treatment group; for daughters, sample sizes are shown in brackets, with values for 150
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restricted and abundant maternal diets listed on the left and right, respectively. B: Feeding 151
schedule (feeds 1–5) during the immature development of A. herbicolus for both mothers and 152
daughters. Since the hatching time of A. herbicolus eggs exceeded 24 h, the first feeding 153
occurred on day 2 to ensure newly hatched larvae could access food. To prevent an 154
accumulation of uneaten prey before larval emergence, the second feeding was administered 155
only after larvae were observed, typically on day 3. Subsequent feedings continued daily until 156
the final prey provision. 157
158
These synchronous cohorts of A. herbicolus eggs were randomly assigned to one of 159
two dietary treatments and reared individually until oviposition (FIGURE S2B), as follows: 160
1. Restricted diet: 30 prey eggs in total during immature development (6 per day for 5 days; 161
FIGURE 1B), and 15 eggs per day during adulthood. 162
2. Abundant diet: 50 prey eggs in total during immature development (10 per day for 5 days; 163
FIGURE 1B), and 40 eggs per day during adulthood. 164
Twenty eggs were allocated to each treatment group as replicates. Reproduction is 165
thelytokous so mating was not required. Upon maturity, females were transferred to new 166
rearing cells, and prey was replenished daily to facilitate oviposition. 167
168
2.3.2 Offspring generation 169
Eggs (<16 h old) laid by mothers were assigned to two measurements: 170
1. Egg size measurement: egg volume (V) was estimated from length (L) and maximum 171
breadth (B) using Narushin’s (2005) formula: V = (0.6057 - 0.0018B)LB2 172
2. Developmental plasticity: daughters were reared individually (FIGURE 1A) and provided 173
with one of five prey densities during immature development: 4, 6, 8, 10, or 12 eggs per 174
day for 5 days (20–60 eggs total; FIGURE 1B). Offspring were classified by maternal age 175
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at oviposition as ‘young’ or ‘old,’ with the threshold defined as half the mean oviposition 176
period of mothers in each dietary treatment group. 177
178
2.4 Data collection 179
Both the mothers and daughters were monitored twice daily (08:00 and 17:30). For mothers, 180
developmental time (egg to adult), prey consumption (number of prey eggs consumed), size 181
at maturity (dorsal plate length), fecundity (lifetime oviposition), and lifespan (egg to death) 182
were recorded. For offspring, hatching success, survival to adulthood, developmental time, 183
prey consumption, and size at maturity were recorded. Adult size for both generations was 184
determined by mounting mature individuals in Hoyer’s medium and examining them under a 185
compound microscope (Walter & Krantz 2009). 186
187
2.5 Statistical analysis 188
Analyses were conducted in R (R Core Team, 2024) in RStudio (version 2024.09.1). 189
Graphics and models were generated using ggplot2 and lme4 (Bates et al., 2015; Wickham, 190
2016). For the maternal generation, two eggs from the abundant group did not hatch, and one 191
individual from the abundant group and two from the restricted group were lost during 192
feeding. The remaining individuals survived to oviposition and were analysed. Maternal life-193
history traits were summarised as means ± standard errors of the mean (SEMs). Generalised 194
linear models (GLMs) with Poisson or quasi-Poisson distributions tested the effect of dietary 195
treatments, with model dispersion verified post hoc. Spearman’s correlations examined the 196
relationships between maternal age, prey consumption, and daily oviposition. Egg volume 197
was analysed with linear mixed-effects models (LMMs), including maternal diet and age as 198
fixed effects and mother as a random effect. 199
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For the offspring generation, logistic regressions tested the effects of maternal diet, 200
maternal age, and offspring prey availability on hatching and survival (binomial response). 201
Developmental time and size at maturity were analysed using LMMs with fixed factors 202
(maternal diet, maternal age, and prey availability), a covariate (prey consumption), and 203
mother as a random factor. Likelihood ratio tests (LRTs) were used to assess model fit. 204
Preliminary models including prey availability showed no significant effect on developmental 205
time (LRT: c² = 4.258, df = 4, P = 0.372) and size at maturity (χ² = 6.174, df = 4, P = 0.187), 206
and prey availability was therefore excluded from the final models. Pearson’s correlations 207
assessed the relationships between prey consumption and developmental traits. Offspring 208
prey consumption was analysed using a Poisson GLM, with maternal diet and age as fixed 209
factors and prey consumption as a covariate. Statistical significance was set at α = 0.05. 210
211
3 RESULTS 212
3.1 Diet-induced influences on maternal parameters 213
Several life-history traits of mothers were significantly influenced by dietary conditions 214
(TABLE S1). Individuals in the restricted diet group exhibited longer developmental and 215
oviposition periods and an extended lifespan, whereas those in the abundant diet group 216
showed higher daily oviposition rates, greater maximum daily fecundity, and larger body 217
size. The post-oviposition period and lifetime fecundity did not differ between treatments, 218
while the pre-oviposition period was marginally non-significant (TABLE S1). 219
Individuals given more prey consumed more during both immature development and 220
adulthood (TABLE S1). After reaching adulthood, daily prey consumption declined with age 221
in both dietary groups (Figure S3). Average daily oviposition ranged from one to two eggs in 222
both treatment groups; in the restricted group, this rate remained consistent throughout the 223
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oviposition period, whereas in the abundant group it declined with maternal age 224
(FIGURE S4). 225
Egg size was significantly influenced by dietary condition (LMM: Wald c² = 57.673, 226
df = 1, P < 0.001) and maternal age at oviposition (Wald c² = 74.691, df = 1, P < 0.001). 227
Mothers on the abundant diet produced larger eggs, and egg size declined with age. A 228
significant interaction between diet and maternal age (Wald c² = 47.163, df = 1, P < 0.001) 229
indicated that egg size decreased more sharply with age in mothers on the restricted diet 230
(FIGURE 2). 231
232
233
FIGURE 2. Egg size (volume) of Amblyseius herbicolus as influenced by maternal diet 234
(restricted or abundant) and age at oviposition. Solid lines indicate regression fits, with 235
shaded areas showing 95% confidence intervals. Regression equation, Pearson’s correlation 236
coefficient (R), and P-value are provided. 237
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238
3.2 Maternal diet and age influences on offspring parameters 239
3.2.1 Hatching and survival to adulthood 240
Offspring were classified by maternal age at oviposition based on mean oviposition periods 241
(TABLE S1). In the restricted group, ‘young’ offspring were derived from eggs laid on days 242
1 to 18, and ‘old’ from day 19 onwards; in the abundant group, ‘young’ were from days 1 to 243
13, and ‘old’ from day 14 onwards. 244
Hatching success was unaffected by maternal diet (logistic regression: Wald 245
c² = 0.001, df = 1, P = 0.972), maternal age at oviposition (Wald c² = 0.576, df = 1, 246
P = 0.448), offspring diet (Wald c² = 0.269, df = 1, P = 0.604), or their interactions 247
(FIGURE 3A). In contrast, survival to adulthood was influenced by offspring diet (Wald 248
c² = 83.683, df = 1, P < 0.001) and maternal age (Wald c² = 7.040, df = 1, P = 0.008), with a 249
significant interaction between maternal age and offspring diet (Wald c² = 9.463, df = 1, 250
P = 0.002). Specifically, offspring from older mothers and those provided more prey had 251
higher survival, particularly under low prey availability (FIGURE 3B). 252
253
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254
FIGURE 3. Hatching rate (A) and survival to adulthood (B) of Amblyseius herbicolus 255
offspring under different offspring prey diets (20–60 eggs) and maternal age/diet treatments. 256
Panels separate restricted and abundant maternal diets. Offspring from young and old 257
mothers are defined as in the text. 258
259
3.2.2 Developmental duration and size at maturity 260
Developmental duration was significantly affected by maternal age (LMM: 261
Wald c² = 38.063, df = 1, P < 0.001) with a significant interaction between maternal age and 262
diet (Wald c² = 21.710, df = 1, P < 0.001), but not maternal diet (Wald c2 = 0.878, df = 1, 263
P = 0.349) and prey consumption (Wald c2 = 1.122, df = 1, P = 0.290). Offspring from older 264
mothers took longer to mature, particularly in the abundant diet group (FIGURE 4). 265
266
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267
FIGURE 4. Developmental duration of offspring in relation to prey consumption, maternal 268
diet, and maternal age at oviposition. Solid lines show regression fits; shaded areas indicate 269
95% confidence intervals. Offspring from young and old mothers are defined as in the text. 270
271
Size at maturity was significantly influenced by prey consumption (LMM: Wald 272
c² = 56.224, df = 1, P < 0.001), maternal age (Wald c² = 4.238, df = 1, P = 0.040), and the 273
interaction between maternal diet and age (Wald c² = 4.167, df = 1, P = 0.041). Larger size 274
was associated with higher prey consumption and older mothers; differences between 275
offspring of young and old mothers were more pronounced in the restricted maternal diet 276
group (FIGURE 5). 277
278
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279
FIGURE 5. Dorsal plate length of offspring in relation to prey consumption, maternal diet, 280
and maternal diet. Solid lines show regression fits; shaded areas indicate 95% confidence 281
intervals. Offspring from young and old mothers are defined as in the text. 282
283
3.2.3 Prey consumption 284
Offspring prey consumption increased with prey availability (GLM: Wald c2 = 859.229, 285
df = 1, P < 0.001). Maternal age at oviposition (Wald c2 = 30.510, df = 1, P < 0.001) and the 286
interaction between maternal diet and age (Wald c2 = 4.288, df = 1, P = 0.038) were also 287
significant: offspring of older mothers consumed less, especially when mothers were on the 288
restricted diet (FIGURE 6). Maternal diet alone had no significant effect (Wald c2 = 1.401, 289
df = 1, P = 0.236). 290
291
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292
FIGURE 6. Offspring prey consumption by prey availability (20, 30, 40, 50, and 60 eggs), 293
maternal diet, and maternal age. Individual points show observations (beeswarm); boxplots 294
indicate median, interquartile range (IQR), and 1.5 × IQR whiskers. Panels separate restricted 295
and abundant maternal diets. Sample sizes (n) are indicated below each box. Offspring from 296
young and old mothers are defined as in the text. 297
298
4 Discussion 299
Our study provides evidence for an inverse Lansing effect in the predatory mite 300
A. herbicolus. Offspring of older mothers showed higher survival to maturity, longer 301
development, larger body size, and reduced prey consumption during development. 302
Moreover, offspring of older mothers exhibited no significant reduction in developmental 303
plasticity compared to those of younger mothers. These findings contrast with the classical 304
Lansing effect and our first hypothesis, but align with studies showing that late-life 305
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reproduction can result in enhanced offspring quality in some species (Marshall et al., 2010; 306
Travers et al., 2021; Anderson et al., 2022). For instance, older spiders (Argiope radon) 307
produce offspring with greater starvation tolerance (Ameri et al., 2019), and beetles 308
(Menochilus sexmaculatus) develop faster when produced by older mothers (Singh et al., 309
2021). Such findings suggest that maternal age effects may represent adaptive shifts in 310
reproductive strategy rather than simple deterioration. Our results indicate a terminal 311
investment strategy rather than senescent decline in A. herbicolus. 312
313
4.1 Maternal investment and offspring performance 314
Maternal diet strongly influenced life-history traits in A. herbicolus. Females on a restricted 315
diet produced fewer eggs per day but extended their oviposition period and lived longer, 316
resulting in lifetime fecundity comparable to females on an abundant diet. This trade-off 317
between current reproduction and survival is consistent with resource-allocation models 318
observed across taxa (Kaitala, 1991; Zera & Harshman, 2001; Lee et al., 2020). 319
Egg size and number were affected by both maternal diet and age. Larger eggs were 320
produced under the abundant diet, which is consistent with other predatory mite species 321
(Walzer & Schausberger, 2015). However, the reduction in egg size and number with 322
advanced maternal age was only observed in those given the abundant diet. Such age-related 323
patterns vary across taxa, with decreases in egg size in Drosophila melanogaster (Bloch Qazi 324
et al., 2017) but increases in ladybirds (Coleomegilla maculata) (Vargas et al., 2012). 325
Interestingly, diet-restricted females showed more stable investment across their reproductive 326
lifespan, and we found no evidence for a size–number trade-off as observed in other species 327
(Gliwicz & Guisande, 1992). 328
Despite reductions in egg size with maternal age, offspring performance was not 329
compromised. Larger eggs are typically associated with enhanced offspring growth, size, and 330
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survival (Fox, 1994; Dias & Marshall, 2010; Rius et al., 2010). Thus, our finding suggests 331
that maternal age effects in A. herbicolus operate independently of egg size. Similar findings 332
have been observed in the soil mite S. berlesei (Benton et al., 2008). Since egg provisioning 333
is an important mechanism underlying maternal age effects (Mousseau & Dingle, 1991; 334
Mousseau & Fox, 1998; Yanchula & Alto, 2021), egg nutrient content and composition, 335
rather than size alone, may be key factors in A. herbicolus. For example, older mothers of the 336
parasitic wasp Eupelmus vuilleti showed reduced egg provisioning with protein, sugar, and 337
lipids, which resulted in a lower nutrient composition at maturity (Muller et al., 2017). 338
Testing whether maternal age alters egg nutrient composition in A. herbicolus remains an 339
important future direction for research. 340
341
4.2 Maternal diet-by-age interactions 342
Maternal diet modulated the age effects on offspring. Differences in survival, size, and prey 343
consumption between offspring of older and younger mothers were most pronounced when 344
mothers had restricted diets. Contrary to our second hypothesis and previous models 345
(Vijendravarma et al., 2010; Hafer et al., 2011; van den Heuvel et al., 2016), offspring from 346
older, diet-restricted mothers had the best overall performance. One possible explanation is 347
that the observed effects are anticipatory, where mothers prime their offspring against 348
resource limitation. Alternatively, it could be that our restricted diet treatment was not 349
sufficiently stressful to elicit phenotypic costs on offspring, and the mild dietary restriction 350
may have buffered negative maternal age effects (Gribble et al., 2014; Hibshman et al., 351
2016). Stronger dietary stress could reverse this pattern, which should be investigated in 352
future experiments. 353
The results of our study also highlight the context-dependence of maternal age effects, 354
consistent with evidence that outcomes can vary across environmental conditions and taxa 355
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(Beckerman et al., 2006; Marshall et al., 2010; Kuijper & Johnstone, 2018; Zirbel & Alto, 356
2018). 357
358
4.3 Proximate mechanisms and ecological implications 359
The most important finding was that offspring of older mothers grew larger while consuming 360
fewer prey, which suggests an increased efficiency of energy conversion (Abrams et al., 361
1996; Arendt, 1997). Whether this reflects altered metabolism, reduced energy expenditure 362
(e.g., foraging activity), or other physiological mechanisms warrants further study. 363
Another possible explanation for reduced prey consumption between offspring of old 364
and young mothers could be the variation in their predation strategy. In arachnids, 365
superfluous killing—killing more prey than consumed—has been documented in both mites 366
and spiders (Metz et al., 1988; Maupin & Riechert, 2001; López‐Mercadal et al., 2024). 367
Offspring of younger mothers might engage more in superfluous killing whereas those of 368
older mothers might not. Although we found no direct evidence of partially consumed prey 369
eggs, this remains a hypothesis for future testing. 370
Reduced prey consumption by the later-produced offspring could provide adaptive 371
benefits. Later-produced offspring may encounter depleted resources because of utilisation by 372
mothers and earlier-produced offspring. Lower consumption requirements may reduce 373
intraspecific competition among siblings and with mothers, which enhances both maternal 374
and offspring survival. As a solitary predator, reduced food demand in the later-produced 375
A. herbicolus could also facilitate dispersal and colonisation of new patches. Maternal age 376
may thus act as a cue of environmental change, enabling offspring to anticipate resource 377
scarcity (Vargas et al., 2012) and the onset of environmental stresses (Rossi et al., 2016). 378
Furthermore, such age-related changes in maternal provisioning strategies may enhance long-379
term fitness by diversifying brood performance (Cameron et al., 2017). 380
preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
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381
4.4 Future directions 382
Our study was conducted in an asexual system, which avoids confounding paternal effects 383
but limits generalisation to sexually reproducing taxa (Castonguay & Angers, 2012; 384
Verhoeven & Preite, 2014). Moreover, prey consumption declined with maternal age in both 385
diet treatment groups. This dynamic could alter effective resource availability (i.e., more 386
leftovers from older individuals) and influence maternal provisioning, potentially 387
contributing to the observed inverse Lansing effect. Future work on sexually reproducing 388
species would help determine whether similar age-related patterns and maternal provisioning 389
dynamics occur under biparental reproduction. 390
The persistence of maternal-age effects across generations remains uncertain. Some 391
studies report only immediate maternal effects, while others document transgenerational 392
persistence (Plaistow et al., 2015; Goos et al., 2019; Wylde et al., 2019). Assessing whether 393
maternal-age effects extend beyond a single generation, and whether these effects are 394
additive or interactive with subsequent generations and environmental factors, can provide 395
important insights into non-genetic inheritance. 396
Lastly, offspring may respond differently to variation in age-related maternal 397
provisioning (Plaistow et al., 2015). Whether the observed inverse Lansing effect in 398
A. herbicolus is a compensatory strategy, and whether this leads to trade-offs in later life, 399
should be examined further. 400
401
5 Conclusions 402
In summary, we observed evidence of an inverse Lansing effect, where offspring of older 403
mothers performed better than those of younger mothers during development. Our study 404
highlights that maternal diet can affect offspring development in A. herbicolus, and that the 405
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22
effect depends strongly on maternal age at oviposition. The interaction between maternal diet 406
and age suggests that maternal reproductive decisions and maternal effects are not static but 407
change over time, and that the timing of oviposition plays a crucial role in shaping offspring 408
outcomes. Maternal age may therefore play a key role in maintaining variation in life 409
histories and should be considered more explicitly when examining maternal effects and 410
offspring performance. 411
412
Limitation
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