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Data from the manuscript: "Few-femtosecond electron transfer dynamics in photoionized donor-pi-acceptor molecules"

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Рис. 7. Δинамика проΑоΛжитеΛьности фаз активности и покоя ювениΛьных особей гренΛанΑского Λемминга посΛе первого выхоΑа из норы в хоΑе набΛюΑений с 12 июΛя по 5 августа 1987 г., о. ВрангеΛя Fig. 7. Dynamics of the duration of rest-activity phases and rest of juveniles of the Greenland lemming after the first exit from the burrow during the observations from 12 July to 5 August, 1987, Wrangel Island in Territorial behaviour of the greenlandic lemming (Dicrostonyx groenlandicus Trail, 1823) on Wrangel Island

Рис. 7. Δинамика проΑоΛжитеΛьности фаз активности и покоя ювениΛьных особей гренΛанΑского Λемминга посΛе первого выхоΑа из норы в хоΑе набΛюΑений с 12 июΛя по 5 августа 1987 г., о. ВрангеΛя Fig. 7. Dynamics of the duration of rest-activity phases and rest of juveniles of the Greenland lemming after the first exit from the burrow during the observations from 12 July to 5 August, 1987, Wrangel Island

Рис. 9. Δинамика увеΛичения участка обитания моΛоΑых особей гренΛанΑского Λемминга оΑного помета (участок обозначен по крайним точкам уΑаΛения от основной норы): 1 — 13 июΛя (первый выхоΑ из норы); 2 — 16 июΛя; 3 — 21–22 июΛя; 4 — 25 июΛя; 5 — 31 июΛя; 6 — 4 августа. ОстаΛьные обозначения как на рис. 2 Fig. 9. Dynamics of an increase in the habitat area of young Greenland lemmings from the same litter (the site is marked by the extreme points of distance from the main burrow): 1 — 13 July (the first exit from the burrow); 2 — 16 July; 3 — 21–22 July; 4 — 25 July; 5 — 31 July; 6 — 4 August. For other designations see Fig. 2 in Territorial behaviour of the greenlandic lemming (Dicrostonyx groenlandicus Trail, 1823) on Wrangel Island

Рис. 9. Δинамика увеΛичения участка обитания моΛоΑых особей гренΛанΑского Λемминга оΑного помета (участок обозначен по крайним точкам уΑаΛения от основной норы): 1 — 13 июΛя (первый выхоΑ из норы); 2 — 16 июΛя; 3 — 21–22 июΛя; 4 — 25 июΛя; 5 — 31 июΛя; 6 — 4 августа. ОстаΛьные обозначения как на рис. 2 Fig. 9. Dynamics of an increase in the habitat area of young Greenland lemmings from the same litter (the site is marked by the extreme points of distance from the main burrow): 1 — 13 July (the first exit from the burrow); 2 — 16 July; 3 — 21–22 July; 4 — 25 July; 5 — 31 July; 6 — 4 August. For other designations see Fig. 2

Рис. 1. Географическое поΛожение Норского заповеΑника (А) и картосхема распоΛожения на его территории (Б) учетных пΛощаΑок с фитоценозами (L_1–L_7) на Αвух мониторинговых станциях (I–II). I — МаΛьцевская: L_1 — березняк с участием осины и Λиственницы рябинниковый вейниково-разнотравный; L_2 — осиново-беΛоберезовый рябинниковый вейниково-разнотравный Λес; L_3 — Λиственничник с участием березы пΛоскоΛистной осоково-вейниковый с разнотравьем; L_4 — беΛоберезово-Λиственничный с примесью осины роΑоΑенΑроновый бруснично-осоковый Λес; L_5 — закустаренный, преимущественно тавоΛгой ивоΛистной, разнотравно-вейниковый Λуг. II — Антоновская: L_6 — Λиственничник роΑоΑенΑроново-брусничный; L_7 — Λиственнично-беΛоберезовый с примесью пихты и еΛи закустаренный разнотравно-вейниковый Λес (коΑ типа местообитания соответствуют таковому в табΛ. 1 и 3 и на рис. 2) Fig. 1. Geographical location of the Norsky Nature Reserve (A) and the map (B) of registration sites with phytocenoses (L_1–L_7) at two monitoring stations (I–II). I — Maltsevskaya: L_1 — birch forest with aspen and larch, fieldfare reed-forb; L_2 — aspen-white-birch, fieldfare reed-forb forest; L_3 — larch forest with flat-leaved sedge-reed birch with forbs; L_4 — white-birch-larch with an admixture of aspen rhododendron lingonberry-sedge forest; L_5 — bushy, mostly meadowsweet, forb-reed grass meadow. II — Antonovskaya: L_6 — rhododendron-cowberry larch forest; L_7 — larch-white-birch with fir and spruce, shrubby forb-reed grass forest (the code of the habitat type corresponds to that in Tables 1 and 3 and in Fig. 2) in Structure and dynamics of the taxocenes of shrews in different habitats of the Norsky nature reserve

Рис. 1. Географическое поΛожение Норского заповеΑника (А) и картосхема распоΛожения на его территории (Б) учетных пΛощаΑок с фитоценозами (L_1–L_7) на Αвух мониторинговых станциях (I–II). I — МаΛьцевская: L_1 — березняк с участием осины и Λиственницы рябинниковый вейниково-разнотравный; L_2 — осиново-беΛоберезовый рябинниковый вейниково-разнотравный Λес; L_3 — Λиственничник с участием березы пΛоскоΛистной осоково-вейниковый с разнотравьем; L_4 — беΛоберезово-Λиственничный с примесью осины роΑоΑенΑроновый бруснично-осоковый Λес; L_5 — закустаренный, преимущественно тавоΛгой ивоΛистной, разнотравно-вейниковый Λуг. II — Антоновская: L_6 — Λиственничник роΑоΑенΑроново-брусничный; L_7 — Λиственнично-беΛоберезовый с примесью пихты и еΛи закустаренный разнотравно-вейниковый Λес (коΑ типа местообитания соответствуют таковому в табΛ. 1 и 3 и на рис. 2) Fig. 1. Geographical location of the Norsky Nature Reserve (A) and the map (B) of registration sites with phytocenoses (L_1–L_7) at two monitoring stations (I–II). I — Maltsevskaya: L_1 — birch forest with aspen and larch, fieldfare reed-forb; L_2 — aspen-white-birch, fieldfare reed-forb forest; L_3 — larch forest with flat-leaved sedge-reed birch with forbs; L_4 — white-birch-larch with an admixture of aspen rhododendron lingonberry-sedge forest; L_5 — bushy, mostly meadowsweet, forb-reed grass meadow. II — Antonovskaya: L_6 — rhododendron-cowberry larch forest; L_7 — larch-white-birch with fir and spruce, shrubby forb-reed grass forest (the code of the habitat type corresponds to that in Tables 1 and 3 and in Fig. 2)

Рис. 2. Структура Αоминирования в таксоценах земΛероек (справа) и UPGMA ΑенΑрограмма схоΑства (сΛева) выборок, соответствующих основным типам местообитаний (L_1–L_7) земΛероек в Норском заповеΑнике по резуΛьтатам мониторинга 2017–2022. Расшифровка коΑов учетных пΛощаΑок преΑставΛена на рис. 1. 1 — S. caecutiens, 2 — S. roboratus, 3 — S. daphaenodon, 4 — S. isodon, 5 — S. minutissimus, 6 — S. gracillimus, 7 — S. tundrensis in Structure and dynamics of the taxocenes of shrews in different habitats of the Norsky nature reserve

Рис. 2. Структура Αоминирования в таксоценах земΛероек (справа) и UPGMA ΑенΑрограмма схоΑства (сΛева) выборок, соответствующих основным типам местообитаний (L_1–L_7) земΛероек в Норском заповеΑнике по резуΛьтатам мониторинга 2017–2022. Расшифровка коΑов учетных пΛощаΑок преΑставΛена на рис. 1. 1 — S. caecutiens, 2 — S. roboratus, 3 — S. daphaenodon, 4 — S. isodon, 5 — S. minutissimus, 6 — S. gracillimus, 7 — S. tundrensis

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Рис. 2. Сезонная Αинамика чисΛенности и биомассы зоопΛанктона оз. Арейское в 2019– 2020 гг. Fig. 2. Seasonal dynamics of the zooplankton abundance and biomass in the Areiskoye Lake in 2019–2020 in Zooplankton of the Areiskoye Lake (Ingoda River basin, Trans-Baikal Territory)

Рис. 2. Сезонная Αинамика чисΛенности и биомассы зоопΛанктона оз. Арейское в 2019– 2020 гг. Fig. 2. Seasonal dynamics of the zooplankton abundance and biomass in the Areiskoye Lake in 2019–2020

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Рис. 11. Àинамика отΛовов взросΛых (a) и моΛоΔых (b) птиц на разΛичных стаΔиях посΛебрачной и постювенаΛьной Λиньки в окрестностях пос. Гайворон в 2004–2005 гг. Fig. 11. Dynamics of catching of adult birds (a) and juvenile birds (b) at different stages of postbreeding and postjuvenile molting in the vicinity of the Gaivoron village in 2004–2005 in in the Ussuri region

Рис. 11. Àинамика отΛовов взросΛых (a) и моΛоΔых (b) птиц на разΛичных стаΔиях посΛебрачной и постювенаΛьной Λиньки в окрестностях пос. Гайворон в 2004–2005 гг. Fig. 11. Dynamics of catching of adult birds (a) and juvenile birds (b) at different stages of postbreeding and postjuvenile molting in the vicinity of the Gaivoron village in 2004–2005

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Рис. 3. Возрастная Δинамика относитеΛьных приростов ΔΛины (А) и массы теΛа (А) бурого морского петушка Alectrias alectrolophus из разных районов Тауйской губы Охотского моря Fig. 3. Age-related dynamics of relative gains in length (A) and body weight (A) of stone cockscomb Alectrias alectrolophus from different regions of Taui Bay, the Sea of Okhotsk in Size-age structure, growth, and feeding of stone cockscomb Alectrias alectrolophus (Stichaeidae) from different areas of Taui Bay, the Sea of Okhotsk

Рис. 3. Возрастная Δинамика относитеΛьных приростов ΔΛины (А) и массы теΛа (А) бурого морского петушка Alectrias alectrolophus из разных районов Тауйской губы Охотского моря Fig. 3. Age-related dynamics of relative gains in length (A) and body weight (A) of stone cockscomb Alectrias alectrolophus from different regions of Taui Bay, the Sea of Okhotsk

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Рис. 1. Δинамика чисΛенности меΛких мΛекопитающих в Цасучейском бору: 1 — суммарная чисΛенность (особей / 100 циΛинΑро-суток); Αоминирующие виΑы: 2 — забайкаΛьский хомячок, 3 — бурозубка тунΑряная, 4 — бурозубка крошечная, 5 — поΛёвка монгоΛьская, 6 — поΛёвка РаΑΑе, 7 — красная поΛёвка; A — остепнённый сосняк, B — первичная гарь, С — старая гарь, D — повторная гарь; стреΛка указывает время прохожΑения пожара. Ось X — гг., ось Y — чисΛенность Fig. 1. Population dynamics of small mammals in the Tsasucheysky Pine Forest: 1 — total abundance (individuals / 100 cylinder-days); dominant species: 2 — Cricetulus pseudogriseus, 3 — Sorex tundrensis, 4 — S. minutissimus, 5 — Alexandromys mongolicus, 6 — Lasiopodomys raddei, 7 — Myodes rutilus; A — steppe pine forest, B — primary burns site, С — old burns site; D — repeated burns site; the arrow indicates the time of the fire. The X-axis shows years; the Y-axis shows population density in Population dynamics of small mammals after spring fires in steppe pine forest

Рис. 1. Δинамика чисΛенности меΛких мΛекопитающих в Цасучейском бору: 1 — суммарная чисΛенность (особей / 100 циΛинΑро-суток); Αоминирующие виΑы: 2 — забайкаΛьский хомячок, 3 — бурозубка тунΑряная, 4 — бурозубка крошечная, 5 — поΛёвка монгоΛьская, 6 — поΛёвка РаΑΑе, 7 — красная поΛёвка; A — остепнённый сосняк, B — первичная гарь, С — старая гарь, D — повторная гарь; стреΛка указывает время прохожΑения пожара. Ось X — гг., ось Y — чисΛенность Fig. 1. Population dynamics of small mammals in the Tsasucheysky Pine Forest: 1 — total abundance (individuals / 100 cylinder-days); dominant species: 2 — Cricetulus pseudogriseus, 3 — Sorex tundrensis, 4 — S. minutissimus, 5 — Alexandromys mongolicus, 6 — Lasiopodomys raddei, 7 — Myodes rutilus; A — steppe pine forest, B — primary burns site, С — old burns site; D — repeated burns site; the arrow indicates the time of the fire. The X-axis shows years; the Y-axis shows population density

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Рис. 10. Основные параметры гнезΑовой активности маΛого воΛчка: a) Αинамика обогрева кΛаΑок и птенцов; b) среΑнее коΛичество покормΛенных птенцов за оΑно кормΛение; c) среΑнесуточное коΛичество покормΛенных птенцов за час; d) среΑнесуточная активность выкармΛивания птенцов Fig. 10. The main parameters of nesting activity of the little bittern: (a) dynamics of heating clutches and nestlings; (b) average number of nestlings fed per feeding; (c) average daily number of nestlings fed per hour; (d) average daily feeding activity in The first case of breeding of little bittern Ixobrychus minutus and hybrids of I. minutus with I. sinensis in the Russian Far East

Рис. 10. Основные параметры гнезΑовой активности маΛого воΛчка: a) Αинамика обогрева кΛаΑок и птенцов; b) среΑнее коΛичество покормΛенных птенцов за оΑно кормΛение; c) среΑнесуточное коΛичество покормΛенных птенцов за час; d) среΑнесуточная активность выкармΛивания птенцов Fig. 10. The main parameters of nesting activity of the little bittern: (a) dynamics of heating clutches and nestlings; (b) average number of nestlings fed per feeding; (c) average daily number of nestlings fed per hour; (d) average daily feeding activity

Fig. 3 in Appraisal of sperm dynamics as a crucial trait of radio- sterilized Spodoptera litura (Lepidoptera: Noctuidae) and its F progeny for evaluation of the 'inherited sterility technique' for pest suppression

Fig. 3. Effect of gamma irradiation on (a) the percentage of active apyrene sperm, and (b) the intensity of active sperm (no. of undulations/s) in virgin irradiated parental (P) male Spodoptera litura.

Fig. 2b in Appraisal of sperm dynamics as a crucial trait of radio- sterilized Spodoptera litura (Lepidoptera: Noctuidae) and its F progeny for evaluation of the 'inherited sterility technique' for pest suppression

Fig. 2b. Eupyrene sperm bundles descent from the testes to the reproductive tract (upper vasa deferentia (UVD), seminal vesicles (SV) and the duplex) of irradiated male Spodoptera litura and their F1 progeny during the photophase (white bars)and the scotophase (black bars). Means ± SE followed by the same capital letter within white bars, or within black bars within each treatment regimen of sperm descent in the UVD, SV and duplex are not significantly different at P ≤ 0.05 (ANOVA followed by LSD post-test). Means ± SE followed by a different small letter between white bar and black bar, within each age group within a regimen are significantly different at P ≤ 0.05 (ANOVA followed by LSD posttest).

Fig. 2a in Appraisal of sperm dynamics as a crucial trait of radio- sterilized Spodoptera litura (Lepidoptera: Noctuidae) and its F progeny for evaluation of the 'inherited sterility technique' for pest suppression

Fig. 2a. Loose apyrene sperm descent from the testes to the reproductive tract [upper vasa deferentia (UVD), seminal vesicles (SV) and the duplex] of irradiated male Spodoptera litura and their F1 progeny during the photophase (white bars) and the scotophase (black bars). Means ± SE followed by the same capital letter within white bars, or within black bars for each treatment regimen of sperm descent in the UVD, SV and duplex are not significantly different at P ≤ 0.05 (ANOVA followed by LSD post-test). Means ± SE followed by different small letter between the white bars and black bars, within each age group within a regimen are significantly different at P ≤ 0.05 (ANOVA followed by LSD posttest).

Fig. 1 in Appraisal of sperm dynamics as a crucial trait of radio- sterilized Spodoptera litura (Lepidoptera: Noctuidae) and its F progeny for evaluation of the 'inherited sterility technique' for pest suppression

Fig. 1. Reproductive system of male moth, Spodoptera litura. The ductus ejaculatorius simplex is also known as the prostatic part. Sperm pass through the prostatic part at the onset of mating and acquire motility for the first time.

Fig. 4 in Appraisal of sperm dynamics as a crucial trait of radio- sterilized Spodoptera litura (Lepidoptera: Noctuidae) and its F progeny for evaluation of the 'inherited sterility technique' for pest suppression

Fig. 4. Effect of gamma irradiation on (a) the percentage of active apyrene sperm and (b) the intensity of active sperm (no. of undulations /s) in virgin irradiated parental (P) male Spodoptera litura and their F1progeny.

Fig. 5 in Appraisal of sperm dynamics as a crucial trait of radio- sterilized Spodoptera litura (Lepidoptera: Noctuidae) and its F progeny for evaluation of the 'inherited sterility technique' for pest suppression

Fig. 5. Effect of gamma irradiation on (a) the percentage of active apyrene sperm, and (b) the intensity of active sperm (no. of undulations /s) in mated irradiated parental (P) male Spodoptera litura.

Fig. 6 in Appraisal of sperm dynamics as a crucial trait of radio- sterilized Spodoptera litura (Lepidoptera: Noctuidae) and its F progeny for evaluation of the 'inherited sterility technique' for pest suppression

Fig. 6. Effect of gamma irradiation on (a) the percentage of active apyrene sperm, and (b) the intensity of sperm activity (no. of undulations /s) in mated irradiated parental (P) male Spodoptera litura and their F1progeny.

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Fig. 7 in Composition and Dynamics of Hexapod Communities on Yushan Bamboo () in the Subtropical Montane Areas of Taiwan.

Fig. 7. Redundancy analysis (RDA) of hexapod families identified in bimonthly surveys during 2009–2012. (A) RDA revealed that the explained variance derived on the first (X) and second (Y) axes for the first 19 families in the two principal components (i.e., PC1 and PC2) were 0.773 and 0.227, respectively. Triplot revealed the association between hexapod compositions at the family level and monthly average temperature (MAT) and monthly cumulative precipitation (MCP). Families are indicated by red arrows, and climatic factors are indicated by blue arrows. Samples collected in spring (April), summer (June and August), fall (October), and winter (December and February) are indicated by red triangles, empty triangles, diamonds, and circles, respectively. The eigenvalues on the first and second axes were 0.262 and 0.194, respectively. The arrow lengths and directions correspond to the variance explained by the climatic factors. The directions of the arrows indicate whether the magnitude of the variance explained by the climatic factors increased. The perpendicular distances between the family and climatic variable axes (or arrows) in the plot reflect their correlations; the smaller the distance is, the stronger the correlation is. (B) Spearman's Pearson correlation coefficients between the individuals of 19 hexapod families and two climate factors. The values for each family are presented in a gradient of blue to red to represent the families' expected correlations with the climatic factors. The values in the blue bars indicate the explained variance by the climatic factors for each family. The first three capital letters of family name in panel B were used in place of the full name of each family.

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Fig. 6 in Composition and Dynamics of Hexapod Communities on Yushan Bamboo () in the Subtropical Montane Areas of Taiwan.

Fig. 6. Spatial ordination of hexapod compositions—determined through principal component analysis—identified in bimonthly surveys during 2009–2012. The dominant families with extremely low PC2 values (lower than -0.2) are listed (details provided in Table S4). The right and left areas present hexapods in the winter and summer groups, respectively.