Fig. 1. Evolution of shrew community structure in the last decadestoothed shrew was represented only by few individualsrecorded in “Codri” forest reserve. Its abundance didn’toverpass 2% from the shrew population. The pigmyand lesser white-toothed shrews had approximately thesame frequency and constituted about 20% from thewhole shrew population.In the 1980’s the abundance of common shrew wasmaintaining at high level and the species constitutedmore than half of shrew population (fig. 1). It was theonly species among shrews that was recorded in forestshelter belts (Munteanu, Savin, 1990). In opposite,the Mediterranean water shrew dominance decreasedbelow 20 %, this species being common only in naturalreserves in biotopes near water sources, while in theother ecosystems it became very rare. The abundanceof Pigmy shrew increased by about 10 %, especially in„Codri” forest reserve in wet biotopes (Averin et al., 1984),but it still was rather rare on the republic territory. Theabundance of Crocidura genus species was very low,below 10 % each species.In 1990’s the changes of economic conditions leadto the changes of ecosystems’ structure and to themodification of the Republic of Moldova landscape. Vastsingle-crop agricultural fields from the agrarian complexof 70-80’s that occupied large territories were dividedin parcels cultivated with various annual, biannual andperennial cultures. Many lands were abandoned anduncultivated. The process of natural habitat destructionwas rather intense. In such stressful conditions the shrewspecies density decreased drastically by comparingwith other mammal groups. In this period the commonshrew proved to be the most well adapted species withthe largest limits of ecological valence. Thus, it hadthe highest abundance among soricid mammals andconstituted almost 80 % from the shrew population. Thedensity of other shrew species was very low: the pigmyshrew constituted 10 %, the Mediterranean water shrew– about 8 %, the lesser white-toothed shrew – about 5%, while the white toothed shrew – only 1-2 % (fig. 1).The last species was very rare in the past century, soit was included in the Red Book of Moldova as criticallyendangered.After 2000 many abandoned lands and reverted totheir more or less natural state as natural biotopes, suchas pastures, meadows, grazing lands etc. At the sametime, the processes of anthropization, urbanization anddegradation of the natural ecosystems occur all over theterritory of the republic. In this context the modification ofthe shrew community’s structure continued.The common shrew remain the dominant species inthe population, but its abundance decreased significantly(to 43 %) by comparing with the end of XXth century.It is more tolerant to the environment conditions andto anthropogenic activity by comparing to other shrewspecies. It was recorded in the majority of studied naturaland anthropogenic biotopes (F=94 %). The pigmy shrewfrequency was also rather high – 88 %, but it is morerare, with the abundance of 35 % (fig. 1). The density ofbicolor white-toothed shrew increased up to 8,8 % and itsfrequency was rather high with the value of 9,7 % while inits preferred habitats the frequency of the species reach42 % (Nistreanu et al., 2008). The lesser white-toothedshrew has the same biotopic preferences as the previousspecies and it was more frequent (17,8 %) and abundant(12,5 %). The Mediterranean water shrew was the rarestshrew among other species after 2000. Its frequencywas very low (below 5 %), it being registered only nearaquatic basins of natural reserves, and the abundancewas of 2,4 %.In 2008 the structure of shrew communities onthe territory of Moldova is totally different (fig. 2). Thedominant species was the lesser white-toothed shrewwith 51.32 %, which constituted more than half of shrewpopulation. Its frequency constituted 40 % in naturalecosystems and more than 85% in urban environment.The species N. anomalus wasn’t registered in any of thestudied ecosystems. The other species had approximatelythe same abundance (fig.2). The trappability index variedfrom 2 % to 16 % from all the micromammal species.In 2009 the proportion of shrew species within thecommunity chanced again. The dominant species was thecommon shrew with over 44%, followed by bicolor whitetoothedshrew, with about 30 % (fig. 2). In opposite to theprevious year C. suaveolens had the lowest abundance.— 149 —
20082009Fig. 2. Structure of shrew communities in the last two yearsIt constituted only 11.11 %, while the pigmy shrewconstituted about 15 %. The trappability index varied from1 % to 15 % from all the micromammal species.We have to mention the high abundance of bicolourwhite-toothed shrew in the last several years. Its densityincreased gradually since the beginning of the XXI centuryand reaches its maximum in 2009. It was recorded notonly in natural and wet biotopes, but also in more aridones and in agocenoses. In abandoned lands the specieswas even more abundant that the common shrew andits trappability index constituted 10 % from all the smallmammals.Like in the previous year the Mediterranean watershrew wasn’t recorded in the studied biotopes. Itsabundance in the republic ecosystems decreaseddrastically in the last 20 years and it becomes a very rareand critically endangered species. This fact is causedby the degradation of wet habitats and of water basinspollution. We recommend it to be introduced in the thirdedition of Red Book of Moldova.ConclusionsThe structure of shrew community showed significantchanges during the last decades. The most well adaptedspecies is the common shrew. The bicolor whitetoothedshrew, which was critically endangered species,introduced in the red Book of Moldova, became one ofthe most common among shrews in the last years. Inopposite the Mediterranean water shrew that was oneof the most abundant in the past century, at present iscritically endangered, because of the destruction andtransformation of its natural habitats. The pygmy andlesser white-toothed shrews are wide spread in varioustypes of ecosystems, but their abundance is always below20%. The shrew species are good ecological indicators.Further measures on the protection of shrew habitatsmust be taken.Bibliography1. Munteanu A. Mamifere. Natura Rezervaţiei „Plaiul Fagului”,2005, p. 244-265.2. Nistreanu V. Soricidele (Soricidae, Insectivora) din colecţiamuzeului Laboratorului Vertebrate Terestre al Institutului de zoologie alA.S.M. VI Conf. of Zoologists of Moldova, Chisinau, 2007, p. 43-44.3. Nistreanu V., Spreading of insectivore species (Erinaceidae,Talpidae, Soricidae, Insectivora) in Nistru river basin. TransboundaryDniester river basin management and the EU Water FrameworkDirective. International Conference, 2-3 October 2007, p. 2<strong>13</strong>-217.4. Nistreanu Victoria, Munteanu A., Savin A., Caraman Natalia,Beneş O., Gheorghiţă S., Burlacu Victoria, Uspenscaia Inga. Datepreliminare privind răspândirea soricidelor (Soricidae, Insectivora)pe teritoriul Republicii Moldova. Simpozion Internaţional consacratjubileului de 60 de ani al academicianului Ion Toderaş. Chişinău, 2008,p. 68-70.5. Nistreanu V. Spreading of shrews from genus Sorex onthe territory of Republic of Moldova. Annual Zoological Congressof “Grigore Antipa” Museum, 12-<strong>13</strong> November 2009, Bucharest,Romania, p.50.6. Аверин Ю.В., Мунтяну А.И., Чегорка П.Т., Гавриленко В.С.,Лункашу М.И., Савин А.И. Млекопитающие. Природа ЗаповедникаКодры. Кишинэу «Штиинца» 1984, стр. 57-64.7. Лозан М.Н. Насекомоядные. Млекопитающие. «Животныймир Молдавии». Кишинэу «Штиинца», 1979, стр. 25-40.8. Лозан М.Н. Насекомоядные млекопитающие Молдавии(Insectivora, Mammalia). Экология птиц и млекопитающих Молдавии.Кишинэу «Штиинца», 1975, стр. 96-118.9. Мунтяну А.И., Савин А.И. Млекопитающие. «Фауна биоценотическихоазисов и ее практическое значение». Кишинэу «Штиинца»,1992, стр. 179-202.10. Нистряну В., Бурлаку В., Караман Н. Распространениебелозубок (Soricidae, Insectivora) на территории Молдовы. Современныепроблемы зоо– и филогеографии млекопитающих. Пенза.15-20 мая, 2009, стр. 60.11. Тихонов И.А., Котенкова Е.В., Успенская И.Г., КоноваловЮ.Н., Бурлаку В.И., Бенеш О.А., Георгица С.Д., Караман Н.К., ТихоноваГ.Н., Хрыстин В.А., Нистреану В., Мунтяну А.И. Грызуны и насекомоядныенезастроенных территорий г. Кишинева. Proceedingsof 4 th International Scientific-Practical Conference “Urboecosystems:problems and Prospects of Development”, Ishim, 19-20 March 2009,p.310-315.12. Тихонов И.А., А.И. Мунтяну, И.Г. Успенская, Ю.Н. Коновалов,В.И. Бурлаку, О.А. Бенеш, С.Д. Георгица, Н.К., Караман, Г.Н.Тихонова,В.А. Хрыстов, В.Б. Нистреану, Е.В. Котенкова. Видовое разнообразиемелких млекопитающих на примере г. Кишинэу. Геоэкологическиеи биоэкологические проблемы Северного Причерноморья. МатериалыIII Межд. научно-практической конференции. 22–23 октябряТирасполь 2009, стр. 200-203.<strong>13</strong>. Тихонова Г.Н., И.А. Тихонов, Е. В. Котенкова, И. Г. Успенская,Ю.Н. Коновалов, В. И. Бурлаку, В. Нистреану, О.А. Бенеш,С.Д. Георгица, Н. К. Караман, В.А. Хрыстов, А.И. Мунтяну. Сравнительныйанализ населения мелких млекопитающих незастроенныхтерриторий двух Европейских городов (Москвы и Кишинева).Diversitatea, valorificarea raţională şi protecţia lumii animale.Simpozionul internaţional consacrat celei de-a 70-a aniversări din ziuanaşterii profesorului universitar Andrei Munteanu. Chişinău, Ştiinţa2009, p. 117-120.— 150 —
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Descrierea CIP a Camerei Nationale
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Уважаемые коллеги,
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доме, в котором мы в
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с малыми восстанов
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Литература1. Жадин
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Рис. 3. Многолетняя
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тера и глубины изме
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ПОДДЕРЖАНИЕ БИОРАЗ
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Таблица 5. Оптималь
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Таблица. Результат
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ФОРМИРОВАНИЕ БИОЦЕ
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Подавляющее больши
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Рис.1. Днестр вблизи
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сопоставимости дан
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А.Н. Бургеля, К.П. Бу
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Выводы1. Уже на само
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тегории, виды и пор
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санитарно-эпидемио
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Таблица 4. Распреде
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реационных, монито
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Шабановой Г.А. и Кух
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могут быть убраны,
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Турунчук. Связь с с
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Праздник «День Рек
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500ЈPРис. Распределе
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Н. Гроссу * , Р. Шакир
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Calitatea apei r. Nistru conform gr
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Карта геохимическо
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лесу был дуб, сегод
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При предварительно
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щих улучшить социа
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ней опасных загряз
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ФотоприложениеФот
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в Украине - одесска
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тия по гидрохимиче
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ветствующих санита
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ния полей, так и для
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В. Экономический ан
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Таким образом, плат
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Рис. 2. Динамика нор
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Табл. 1а. Статистиче
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Выводы1. Наибольшее
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Для днестровской в
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ЭКОЭТИЧЕСКОЕ ВОСПИ
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гормоны (в незначит
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ПРОТОКОЛ ПО ПРОБЛЕ
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воды ежегодно умир
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РАЗРАБОТКА ПЛАНОВ
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ставляет материаль
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• Совершенствован
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«Алые паруса». Таки
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which the Committee is then require
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нием, культурой и х
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Сброшенный на 50 м б
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СТРУКТУРА ГЕОИНФОР
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4. Пространственная
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На фазе пика числен
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А.А. Тищенков, В.В. М
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Распределение видо
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цветковый (ККП, ЧКУ,
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очередной задачей
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схемой планировани
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эксплуатационным п
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ледствия от урбани
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ОСНОВНЫЕ ФОРМЫ ДЕГ
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УЧАСТИЕ НЕПРАВИТЕЛ
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струкции как от сбр
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Рогоз широколистны
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В рамках первых тре
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Основные экскурсио
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2. Кравченко Е.Н. При
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Decision-Maker user group are respo
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может ее запускать,
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поражения населени
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мость разработки н
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Биология. Подорожн
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банизированных тер
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Результаты исследо
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Рис.1. Сезонная дина
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Молдовы и Приднест
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Рис. 1. Численность
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жений, в том числе э
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КОНСТИТУЦИОНАЛЬНА
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В настоящее время б
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8. Суворцева В.Ю., Ру
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Окончание табл. 2Ок
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содержаниеПРЕДИСЛ
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А.П. Погребняк, В.Ф.
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Научное изданиеБАС