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Journal of Medicine and Pharmacy","Tạp chí Y Dược học Cần Thơ",{"EN":487,"VI":488},"\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">04\u002F10\u002F2015 Ministry of Information and Communications allowed Can Tho journal of medicine and pharmacy to operate (102 \u002FGP-BTTTT)\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">07\u002F16\u002F2015 Can Tho journal of medicine and pharmacy is internationally recognized: ISSN 2354-1210\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">In 2016, The journal has been included in the list of medical science journals by The State Council for professorship which is awarded a work score of 0-0.5 points for a published article.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Can Tho Journal of Medicine and Pharmacy welcome original works that haven’t been submitted or published in other medical journals. Posts must contain content related to one of the journal’s categories.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">The content published\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">The journal is divided into 3 categories:\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">- Scientific research article: are valuable scientific works, which have been researched and accepted.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">- Overview of medicine, biology and pharmacy: serving the objective of continuing training in the fields of medicine, biology and pharmacy; to systematize classical and modern knowledge.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">- Update information on new knowledge about medicine, biology, pharmacy in the country and in the world.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Scope\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">- Publication and introduction of scientific research in the fields:\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">+ Medicine (internal medicine, surgery, pediatrics, obstetrics and gynecology, odonto-stomatology, laboratory, oncology, traditional medicine, nursing).\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">+ Biology (genetics, biotechnology).\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">+ Pharmacology (pharmaceutics, drug quality analysis-control, synthetic pharmaceutical chemistry, biochemistry, pharmacognosy, botany, clinical pharmacy).\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">- To enhance the quality of undergraduate, postgraduate education, scientifically researching and meet the necessary treatment in hospital.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">- Introducing the updated domestic and oversea information about science technology to promote scientific research and exchanging technology in local, other universities.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">- Exchanging pharmaceutical and medical information for social health developing in the Mekong Delta and Vietnam.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">The object\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Postgraduate students, student of Can Tho University of Medicine and Pharmacy, scientists from schools, research institutes, hospitals, health centers, pharmaceutical companies of the Mekong Delta; other provinces and regions in Vietnam and other country.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Address\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Headquarters of Can Tho Journal of Medicine and Pharmacy, located Scientific Research and International Cooperation Office: 179 Nguyen Van Cu Street, An Khanh Ward, Ninh Kieu District, Can Tho City, Vietnam.\u003C\u002Fspan>\u003C\u002Fp>","\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Ngày 16\u002F7\u002F2015, Tạp chí Y Dược học Cần Thơ được cấp chỉ số quốc tế: ISSN 2354-1210.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Từ tháng 4\u002F2016, Tạp chí đã được Hội đồng Giáo sư ngành Y đưa vào danh sách các tạp chí khoa học Y học được tính điểm công trình 0-0,5 điểm cho một bài báo đăng.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Năm 2020 Tạp chí Y Dược học Cần Thơ đã được phê duyệt vào danh mục của các Hội đồng Giáo sư ngành Dược học được tính điểm công trình 0-0,5 điểm cho một bài báo đăng.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tạp chí Y Dược học Cần Thơ ra 12 số\u002Fnăm, 180-200 trang\u002Fsố.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Từ tháng 12\u002F2022 Tạp chí Y Dược học Cần Thơ là thành viên của hệ thống Crossref và từ tháng 01\u002F2023 tạp chí thực hiện bình duyệt online kín 2 chiều nhằm tăng tính minh bạch, tin cậy của các công trình nghiên cứu khoa học và đảm bảo tốt nhất chất lượng khoa học của bài viết.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tôn chỉ, mục đích và phạm vi của tạp chí\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tôn chỉ và mục đích hoạt động của tạp chí: xuất bản nhằm mục đích phổ biến kết quả từ các đề tài nghiên cứu khoa học; giao lưu trao đổi khoa học, chia sẻ kinh nghiệm, học tập, đồng thời cập nhật thông tin khoa học mới trong các lĩnh vực y, sinh, dược học trong và ngoài nước.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Phạm vi của tạp chí: Tạp chí xuất bản được chia thành 3 chuyên mục: (i) Bài báo nghiên cứu khoa học là kết quả công trình nghiên cứu khoa học có giá trị đã được triển khai nghiên cứu, (ii) Bài tổng quan y, sinh, dược học: phục vụ mục tiêu đào tạo liên tục trong lĩnh vực y, sinh, dược học; nhằm hệ thống hóa những kiến thức kinh điển và hiện đại; (iii) Thông tin cập nhật kiến thức mới về y, sinh, dược học trong nước và trên thế giới.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Chính sách truy cập mở\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tạp chí Y Dược học Cần Thơ áp dụng chính sách truy cập mở đối với các bài báo đã xuất bản đến với độc giả, nhằm mở rộng cơ hội tiếp cận các kết quả nghiên cứu chất lượng cao và tăng cường trao đổi kiến thức. Tạp chí đăng tải trực tuyến (miễn phí) toàn văn các bài báo được công bố trên website của Tạp chí (https:\u002F\u002Ftapchi.ctump.edu.vn).\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Đạo đức xuất bản\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tạp chí Y Dược học Cần Thơ cam kết tuân thủ đạo đức xuất bản phù hợp với các hướng dẫn và tiêu chuẩn của the Committee on Publication Ethics (COPE), tuân thủ các nguyên tắc của COPE’s Core Practices, Best Practices Guidelines for Journal Editors và Guidelines on Good Publication Practices.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Bản thảo bài báo chỉ được chấp nhận khi được tác giả chịu trách nhiệm chính cam kết các nội dung sau: Các nội dung của bản thảo chưa được đăng tải toàn bộ hoặc một phần ở các tạp chí khác; Tất cả các tác giả đều có đóng góp một cách đáng kể vào quá trình nghiên cứu hoặc chuẩn bị bản thảo và cùng chịu trách nhiệm về các nội dung của bản thảo; Tuân thủ các biện pháp đảm bảo đạo đức nghiên cứu (ví dụ thỏa thuận đồng ý tham gia nghiên cứu).\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Cam kết bảo mật\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tạp chí cam kết thực hiện và tuân thủ các quy định của luật và các văn bản hướng dẫn liên quan đến bảo mật thông tin cá nhân trên không gian mạng. Các thông tin mà người dùng (tác giả, độc giả, biên tập viên, người phản biện) nhập vào các biểu mẫu trên Hệ thống Quản lý xuất bản trực tuyến của tạp chí chỉ được sử dụng vào các mục đích đã được tuyên bố rõ ràng và sẽ không được cung cấp cho bất kỳ bên thứ ba nào khác, hay dùng vào bất kỳ mục đích nào khác.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Phí gửi bài\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Lệ phí gửi đăng bài: 1.000.000đ\u002Fbài báo\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Lệ phí gửi đăng nhanh: 1.500.000đ\u002Fbài báo\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Đối với tác giả là cán bộ viên chức thuộc Trường Đại học Y Dược Cần Thơ thì được hỗ trợ 50% lệ phí gửi đăng bài.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Đối với sinh viên thực hiện đề tài nghiên cứu khoa học cấp trường được hỗ trợ 100% lệ phí đăng bài ( Tác giả gửi đính kèm “ Quyết định về việc giao tổ chức thực hiện đề tài nghiên cứu khoa học cấp Trường của sinh viên”).\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Hình thức nộp lệ phí:\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">1. Tiền mặt:\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Nộp trực tiếp tại Phòng Tài chính - Kế toán, Trường Đại học Y Dược Cần Thơ, số 179 Nguyễn Văn Cừ, P. An Khánh, Q. Ninh Kiều, thành phố Cần Thơ.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">2. Chuyển khoản:\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tên Tài khoản: Trường ĐHYD Cần Thơ, Số TK: 0111000115668, tại ngân hàng Vietcombank chi nhánh Cần Thơ.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Thời gian: Áp dụng từ ngày 01\u002F02\u002F2023.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">* Phí gửi bài không được hoàn trả khi bài viết bị từ chối hoặc tác giả xin rút bài viết.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Quy trình phản biện bài báo\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tạp chí Y Dược học Cần Thơ thực hiện quy trình phản biện kín hai chiều nghiêm ngặt. Danh tính của những người phản biện không được tiết lộ cho các tác giả và ngược lại. Quy trình thẩm định bài báo đăng gồm các bước sau:\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tiếp nhận bản thảo\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Tác giả liên hệ gửi bản thảo đến Tạp chí qua hệ thống trực tuyến tại website: https:\u002F\u002Ftapchi.ctump.edu.vn. Hướng dẫn về cách đăng ký, gửi bài và chuẩn bị bản thảo được cung cấp trên website của Tạp chí.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Sàng lọc sơ bộ\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Sau khi Tòa soạn nhận được bài báo của tác giả, Ban Thư ký sẽ tiến hành kiểm tra sơ bộ bài báo (các yêu cầu về nội dung và hình thức). Những bài báo không đúng quy cách hoặc có nội dung không phù hợp hoặc vi phạm bản quyền sẽ bị từ chối (Ban Thư ký thông báo phản hồi đến tác giả trong vòng 1 tuần). Những bài báo đủ điều kiện, được Ban Thư ký tòa soạn chuyển đến Ban Biên tập có cùng chuyên môn với nội dung bài báo để đề xuất người phản biện. Thời gian kể từ khi Ban Biên tập nhận bài báo đến khi đề xuất người phản biện bài báo chậm nhất là 5 ngày.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Vòng phản biện\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">1. Ban Thư ký gửi bài và yêu cầu phản biện đến 02 phản biện độc lập.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">2. Các phản biện gởi nhận xét cho Ban Thư ký. Thời gian từ khi gửi bài cho phản biện đến khi nhận ý kiến của phản biện tối đa là 20 ngày.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Xử ký kết quả phản biện\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">1. Nếu ý kiến đồng ý cho đăng và không cần chỉnh sửa, Ban Thư ký tiếp tục đăng bài theo qui trình.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">2. Nếu ý kiến đồng ý đăng và cần chỉnh sửa, Ban Thư ký sẽ thông tin đến tác giả chỉnh sửa theo yêu cầu của người phản biện. Thời gian chỉnh sửa và gửi lại kéo dài không quá 2 tuần, từ khi tác giả bài báo nhận được thông tin (Quá trình này có thể lặp lại tối đa 2 lần\u002F1 bài báo). Khi có sự thống nhất, đồng ý của người phản biện; bài báo được tiếp tục đăng theo qui trình.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">3. Những bài báo có chất lượng không đạt yêu cầu, cả 2 phản biện không đồng ý cho đăng sẽ bị Tòa soạn từ chối đăng.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">Xuất bản\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">1. Ban Thư ký tổng hợp các bản thảo đã được tác giả hoàn thiện sau thẩm định trình Ban Biên tập xem xét, Tổng Biên tập phê duyệt, quyết định bài đăng theo các tiêu chí: sự phù hợp nội dung với tôn chỉ và mục đích, thể loại bài viết (ưu tiên các bài có bài có nghiên cứu chuyên sâu, hàm lượng khoa học cao), đóng góp mới bài báo, bài báo được ưu tiên đăng trong số gần nhất của Tạp chí theo thứ tự: tính thời sự, chất lượng bài báo và thời gian gửi bài.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">2. Ban Biên tập và Ban Thư ký biên tập bản thảo, chế bản, đọc rà soát lỗi. Thời gian hoàn thành từ 10-15 ngày.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">3. Ban Thư ký có trách nhiệm thông báo cho tác giả bài báo (bằng e-mail) về tình hình phê duyệt bài báo, thời gian, số kỳ, tập xuất bản bài báo theo qui định.\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>\u003Cp>\u003Cspan style=\"color: rgb(0, 0, 0);\">4. Danh sách bài báo theo số Tạp chí được in ấn và phát hành trong năm định kỳ được công bố chính thức trên website: https:\u002F\u002Ftapchi.ctump.edu.vn\u003C\u002Fspan>\u003C\u002Fp>\u003Cp>\u003Cbr>\u003C\u002Fp>",{"VOID":490},"wcQ1uqwAAAAJ","2023-05-30T08:17:21.868+00:00",[],[494],{"id":495,"createTime":28,"updateTime":28,"relativeEntities":496,"slug":28,"properties":497,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":507,"parentIds":508,"statistic":28},"6413896b-eca9-442b-a73f-182a58a0ce40",[],{"title":498,"address":501,"country":504,"abbreviation":505},{"EN":499,"VI":500},"Can Tho University of Medicine and Pharmacy","Trường Đại học Y Dược Cần Thơ",{"EN":502,"VI":503},"No 179, Nguyen Van Cu street, An Khanh ward, Ninh Kieu district, Can Tho city, Vietnam","Số 179, đường Nguyễn Văn Cừ, phường An Khánh, quận Ninh Kiều, thành phố Cần Thơ, Việt Nam",{"VOID":15},{"VOID":506},"ctump","http:\u002F\u002Fwww.ctump.edu.vn\u002F",[],[],"https:\u002F\u002Ftapchi.ctump.edu.vn\u002Findex.php\u002Fctump",{"impactFactor":32,"impactFactorByYear":512,"i10Index":32,"i10IndexLast5Year":32,"totalPublication":514,"totalPublicationByYear":515,"totalCitation":520,"totalCitationByYear":521,"totalCitationPerPublication":108,"totalCitationPerPublicationByYear":523,"hindexLast5Year":45,"hindex":45},{"2022":513,"2023":111,"2024":106},0.01,1556,{"2020":47,"2021":516,"2022":517,"2023":518,"2024":519,"2025":122},57,306,801,358,161,{"2021":146,"2022":280,"2023":522},99,{"2021":524,"2022":318,"2023":104},0.23,{"impactFactor":28,"impactFactorByYear":28,"i10Index":123,"i10IndexLast5Year":123,"totalPublication":526,"totalPublicationByYear":527,"totalCitation":526,"totalCitationByYear":528,"totalCitationPerPublication":40,"totalCitationPerPublicationByYear":531,"hindexLast5Year":49,"hindex":49},476,{"0":205,"2019":123,"2021":139,"2022":459,"2023":451,"2024":357,"2025":49,"2026":48},{"2021":42,"2022":123,"2023":161,"2024":529,"2025":360,"2026":530},136,83,{"2021":105,"2022":513,"2023":532,"2024":127,"2025":533,"2026":534},0.62,25.43,13.83,{"id":536,"createTime":537,"updateTime":382,"relativeEntities":538,"slug":539,"properties":540,"entityType":25,"verifyStatus":26,"verifyTime":28,"verifyNote":28,"languages":552,"translateLanguages":28,"viewCount":133,"subjectFields":553,"manageAffiliations":554,"indexDatabases":555,"url":556,"thumbnailPath":557,"statistic":558,"gsStatistic":594,"type":55,"analyzePriority":28},"6984a56a-db70-403b-9cc4-4013e1ceaffa","2023-05-09T06:47:40.346+00:00",[],"T%E1%BA%A1p%20ch%C3%AD%20Nghi%C3%AAn%20c%E1%BB%A9u%20n%C6%B0%E1%BB%9Bc%20ngo%C3%A0i",{"country":541,"issn":542,"title":544,"introduce":547,"gsId":550},{"VOID":15},{"VOID":543},"25252445",{"EN":545,"VI":546},"VNU Journal of Foreign Studies","Tạp chí Nghiên cứu nước ngoài",{"EN":548,"VI":549},"{\"ops\":[{\"insert\":\"\\n\\nThe \\n\"},{\"attributes\":{\"italic\":true},\"insert\":\"VNU Journal of Science\"},{\"insert\":\"\\n was established in 1985 for the publication of national and international research papers in all fields of natural sciences and technology, social sciences and humanities. 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The strains were divided into seven groups based on major morphological and physiological properties. Taxonomic allocation of the groups was verified by guanine+cytosine contents of DNA. Except for one group, which may be assumed to include bacteria belonging to the genera Flavobacterium and Cytophaga, the various groups were taxonomically united. The distribution of the groups changed with soil improvement. Pseudomonads predominated in unimproved soil, but Flavobacterium and Cytophaga spp. were predominant in the most improved soil. As all the strains were non-fermentative by Hugh and Leifson's test, API 20NE identification was applied. However, many strains were misidentified by this system, especially in the Flavobacterium and Cytophaga spp. group. For ecological studies, the strains were classified to species level by the API 20 NE system and by the results of a combination of guanine+cytosine (mol%) and isoprenoid quinone data. The pattern of distribution of the bacteria on the root surface of wheat varied at species level within one genus depending on soil conditions.",{"EN":1044},"Gram-negative bacterial flora on the root surface of wheat (Triticum aestivum) grown under different soil conditions",{"VOID":1046},"Ausubel FM, Brent R, Kingston RE, Moore DD, Seidman JG, Smith JA, Struhl K (eds) (1987) Miniprep of bacterial genomic DNA. In: Current protocols in molecular biology 2.4.2. John Wiley and Sons, New York Chichester Brisbane Toronto Singapore\nBrock TD, Madigan MT (1988) The bacteria. In: Biology of the microorganisms. Prentice Hall, Englewood Cliffs, MJ, pp 683–788\nCase CL, Johnson TR (1984) Gram-staining. In: Laboratory experiments in microbilogy. Benjamin\u002FCummings Publishing Company, Inc., Menlo Park, California, Reading, Massachusetts, London Amsterdam Don Mills Ontario Sydney, pp 23–25\nCollins MD, Johnes D (1981) Distribution of isoprenoid quinones structural types in bacteria and their taxonomic implications. Microbial Rev 45:316–354\nCurl EA, Truelove B (1986) The rhizosphere. Springer-Verlag, Berlin Heidelberg New York Tokyo, pp 113–129\nGoto M, Takikawa Y (1984) Methods for identification of plant pathogenic bacteria (2). Plant Protect 38:385–389 (in Japanes)\nJiang HY, Sato K (1992) Fluctuations in bacterial populations on the root surface of wheat (Triticum aestivum L.) grown under different soil conditions. Biol Fertil Soils 14:246–252\nJiang HY, Sato K (1994) Interrelationships between bacterial, populations on the root surface of wheat and growth of plants. Soil Sci Plant Nutr 40:683–689\nKleeberger A, Castorph H, Klingmuller W (1983) The rhizosphere microflora of wheat and barley with special reference to Gram-negative bacteria. Arch Microbiol 136:306–311\nKloepper JW, Scher FM, Laliberte M, Zaleska I (1985) Measuring the spermosphere colonizing capacity (spermosphere competence) of bacterial inoculants. Can J Microbiol 31:926–929\nKrieg NR, Holt JG (ed) (1984) Bergey's Manual of Systematic Bacteriology, vol. 1. Wiliams and Wilkins, Baltimore Hong Kong London Sydney\nLorch H-J, Benckiser G, Ottow JCG (1995) Basic method for counting microorganisms in soil and water. In: Alef K, Nannipieri P (eds) Methods in applied soil microbiology and biochemistry. Academic Press, London, pp 146–161\nOyaizu H, Komagata K (1981) Chemotaxonomic and phenotypic characterization of the strains of species in the Flavobacterium-Cytophaga complex. J Gen Appl Microbiol 25:57–107\nRovira AD (1965) Interaction between plant roots and soil microorganisms. Annu Rev Microbiol 19:241–266\nSchank SC, Weir KL, MacRae IC (1981) Plant yield and nitrogen content of a digitgrass in response to Azospirillum inoculation. Appl Environ Microbiol 41:342–345\nShewan JM, McMeekin TA (1983) Taxonomy and ecology of Flavobacterium and related genera. Annu Rev Microbiol 37:233–252\nTien TM, Gaskins MH, Hubbel DH (1979) Plant growth substances produced by Azospirillum brasilense and their effect on the growth of pearl millet (Pennisetum americanum L.) Appl Exp Microbiol 37:1016–1024",{"VOID":1048},"10.1007\u002FBF00335955","PUBLICATION","Auto Verify","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002FBF00335955",[1053,1069],{"id":1054,"sortIndex":32,"researcher":28,"roles":1055,"affiliations":1057,"properties":1066},"4389b77b-7aba-42cb-8ccd-c423139a5f7e",[1056],"AUTHOR",[1058],{"id":1059,"sortIndex":32,"affiliation":1060,"properties":28},"b8c6fd82-3fe9-4052-8341-049954a5068d",{"id":1059,"createTime":28,"updateTime":28,"relativeEntities":1061,"slug":28,"properties":1062,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":1065,"statistic":28},[],{"title":1063},{"VI":1064},"Laboratory of Soil Microbiology, Institute of Genetic Ecology, Tohoku University, Sendai, Japan",[],{"title":1067},{"VI":1068},"K. 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transfer between introduced and indigenous bacteria in leaf litter, soil and vermicompost as affected by soil invertebrates",{"VOID":1152},"10.1007\u002Fs003740050480",{"EN":1154}," Plasmid transfer between introduced strains of Pseudomonas stutzeri JM302 (pLV1013), Pseudomonas putida PAW340 (pLV1017), Pseudomonas aeruginosa PAO5 (RP4), and Enterobacter cloacae MF10 (RP4), all of them harbouring genetically modified or naturally occurring plasmids and bacteria indigenous to oak leaf litter, soddy-podzolic soil or vermicompost was monitored using non-sterile laboratory microcosms inhabited by the millipede Pachyiulus flavipes, the woodlouse Armadillidium vulgare, or the earthworms Aporrectodea caliginosa and Eisenia fetida, respectively. Plasmid transfer from genetically modified Streptococcus faecalis JH2-2 (pAMβ1) to Bacillus thuringiensis var. israelensis 1-5 under similar conditions was also followed. A recombinant conjugative plasmid (pLV1017) encoding resistance to antibiotics and expressing catechol 2,3-dioxygenase was transferred into two facultatively anaerobic gram-negative bacteria, isolated from the excrement of A. vulgare. Presumed transconjugants of the facultatively anerobic gram-negative bacteria given above were isolated from the leaves and soil (four strains) and the excrement of the invertebrates (11 strains). They carried the same plasmids and exhibited the same enzymatic activity as the respective inoculant strains; for most of them, however, DNA fingerprints were slightly different. Transfer from S. faecalis JH2-2 to B. thuringiensis var. israelensis of a naturally occurring plasmid, pAMb1, encoding resistance to erythromycin was observed in vermicompost.","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs003740050480",[1157,1172,1187,1200,1215,1228,1241],{"id":1158,"sortIndex":32,"researcher":28,"roles":1159,"affiliations":1160,"properties":1169},"331b17ce-86cd-4e19-8c91-e9e629206692",[1056],[1161],{"id":1162,"sortIndex":32,"affiliation":1163,"properties":28},"80f487a3-94a7-48ed-a7b1-f568cbeee67e",{"id":1162,"createTime":28,"updateTime":28,"relativeEntities":1164,"slug":28,"properties":1165,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":1168,"statistic":28},[],{"title":1166},{"VI":1167},"Department of Soil Biology, Faculty of Soil Science, Moscow Lomonosov State University, Vorobjevy Gory, SU-119899 Moscow, Russia, , RU",[],{"title":1170},{"VI":1171},"B. 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manure to temperate agricultural soils in the fall season is often justified by the assumption that mineral nitrogen (N) is stable in frozen soils, although pulses of nitrous oxide (N2O) are emitted when the soil thaws during winter months. Nitrous oxide loss was monitored during three freeze-thaw cycles in agricultural soils that received manure and had a growing cover crop before they were frozen. Soil was mixed with N fertilizer treatments (none, liquid dairy manure, solid dairy manure, or urea) and packed in 0.2-L pots, half of which were planted with an annual ryegrass (Lolium multiflorum Lam.) cover crop. After 3 weeks, pots were transferred to a freezer at − 4 °C, or left in a refrigerator at + 4 °C. Frozen pots were thawed at + 4 °C. Production of N2O was measured after 0, 3, 6, and 9 h of thawing; then the pots were destructively sampled to determine the soil mineral N concentration. The N fertilizer and cover crop treatments did not affect N2O production, and only 14% of the variation in N2O production was explained by soil mineral N concentration. However, there was a 6–9-fold increase in N2O production, relative to soil mineral N, in pots that underwent freeze-thaw cycles compared to pots that were left at + 4 °C. It appears that N2O was produced in frozen soils at − 4 °C, trapped under ice, and subsequently released when the soils thawed at + 4 °C, suggesting that N2O-producing reactions do not stop when manured soils are frozen.",{"EN":1322},"Freeze-thaw cycles release nitrous oxide produced in frozen agricultural soils",{"VOID":1324},"Beaulieu MS (2004) Manure management in Canada, vol 1. Farm Environmental Management in Canada, Ottawa\nCavigelli MA, Parkin TB (2012) Chapter 9 - Cropland management contributions to greenhouse gas flux: Central and Eastern U.S. In: Franzluebbers AJ, Follett RF (eds) Managing Agricultural Greenhouse Gases. Academic Press, San Diego, pp 129–165\nChapuis-Lardy L, Wrage-Mönnig N, Metay A, Chotte J-L, Bernoux M (2007) Soils, a sink for N2O? A review. Global Change Biol 13:1–17\nChen Y, Tessier S, MacKenzie AF, Laverdière MR (1995) Nitrous oxide emission from an agricultural soil subjected to different freeze-thaw cycles. Agric, Ecosyst Environ 55:123–128\nClark K, Chantigny MH, Angers DA, Rochette P, Parent L-É (2009) Nitrogen transformations in cold and frozen agricultural soils following organic amendments. Soil Biol Biochem 41:348–356\nCober JR, Macrae ML, Van Eerd LL (2018) Nutrient release from living and terminated cover crops under variable freeze-thaw cycles. Agron J 110:1036–1045\nCongreves KA, Wagner-Riddle C, Si BC, Clough TJ (2018) Nitrous oxide emissions and biogeochemical responses to soil freezing-thawing and drying-wetting. Soil Biol Biochem 117:5–15\nDeLuca TH, Keeney DR, McCarty GW (1992) Effect of freeze-thaw events on mineralization of soil nitrogen. Biol Fertil Soils 14:116–120\nEghball B (2000) Nitrogen mineralization from field-applied beef cattle feedlot manure or compost. Soil Sci Soc Am J 64:2024–2030\nEghball B, Wienhold BJ, Gilley JE, Eigenberg RA (2002) Mineralization of manure nutrients. J Soil Water Conserv 57:470–473\nEjack L, Whalen JK, Madramootoo CA (2021) Carbon availability limits the denitrification potential of sandy loam soil from corn agroecosystems with long-term tillage and residue management. Can J Soil Sci 101:5. https:\u002F\u002Fdoi.org\u002F10.1139\u002Fcjss-2020-0097\nElliott AC, Henry HAL (2009) Freeze-thaw cycle amplitude and freezing rate effects on extractable nitrogen in a temperate old field soil. Biol Fertil Soils 45:469–476\nGao D, Zhang L, Liu J, Peng B, Fan Z, Dai W, Jiang P, Bai E (2018) Responses of terrestrial nitrogen pools and dynamics to different patterns of freeze-thaw cycle: a meta-analysis. Global Change Biol 24:2377–2389\nGillam KM, Zebarth BJ, Burton DL (2008) Nitrous oxide emissions from denitrification and the partitioning of gaseous losses as affected by nitrate and carbon addition and soil aeration. Can J Soil Sci 88:133–143\nGuo XB, Drury CF, Yang XM, Reynolds WD, Zhang RD (2011) Influence of current and previous crops on soil basal and potential denitrification rates. Biol Fertil Soils 47:937–947\nHan Z, Walter MT, Drinkwater LE (2017) N2O emissions from grain cropping systems: a meta-analysis of the impacts of fertilizer-based and ecologically-based nutrient management strategies. Nutr Cycl Agroecosys 107:335–355\nHenry HAL (2007) Soil freeze-thaw cycle experiments: trends, methodological weaknesses and suggested improvements. Soil Biol Biochem 39:977–986\nHu HW, Chen D, He JZ (2015) Microbial regulation of terrestrial nitrous oxide formation: understanding the biological pathways for prediction of emission rates. FEMS Microbiol Rev 39:729–749\nJayasundara S, Wagner-Riddle C, Parkin G, Lauzon J, Fan MZ (2010) Transformations and losses of swine manure 15N as affected by application timing at two contrasting sites. Can J Soil Sci 90:55–73\nKariyapperuma KA, Wagner-Riddle C, Furon AC, Li CS (2011) Assessing spring thaw nitrous oxide fluxes simulated by the DNDC model for agricultural soils. Soil Sci Soc Am J 75:678–690\nKool DM, Dolfing J, Wrage N, Van Groenigen JW (2011) Nitrifier denitrification as a distinct and significant source of nitrous oxide from soil. Soil Biol Biochem 43:174–178\nKoponen HT, Flöjt L, Martikainen PJ (2004) Nitrous oxide emissions from agricultural soils at low temperatures: a laboratory microcosm study. Soil Biol Biochem 36:757–766\nLi C, Aber J, Stange F, Butterbach-Bahl K, Papen H (2000) A process-oriented model of N2O and NO emissions from forest soils: 1. model development. J Geophys Res-Atmos 105:4369–4384\nLi X, Sørensen P, Olesen JE, Petersen SO (2016) Evidence for denitrification as main source of N2O emission from residue-amended soil. Soil Biol Biochem 92:153–160\nLudwig B, Wolf I, Teepe R (2004) Contribution of nitrification and denitrification to the emission of N2O in a freeze-thaw event in an agricultural soil. J Plant Nutr Soil Sci 167:678–684\nMorkved PT, Dorsch P, Henriksen TM, Bakken LR (2006) N2O emissions and product ratios of nitrification and denitrification as affected by freezing and thawing. Soil Biol Biochem 38:3411–3420\nNannipieri P, Penton CR, Purahong W, Schloter M, van Elsas JD (2019) Recommendations for soil microbiome analyses. Biol Fertil Soils 55:765–766\nPattey E, Blackburn LG, Strachan IB, Desjardins R, Dow D (2008) Spring thaw and growing season N2O emissions from a field planted with edible peas and a cover crop. Can J Soil Sci 88:241–249\nPelster DE, Chantigny MH, Rochette P, Angers DA, Laganière J, Zebarth B, Goyer C (2013) Crop residue incorporation alters soil nitrous oxide emissions during freeze-thaw cycles. Can J Soil Sci 93:415–425\nPelster DE, Chantigny MH, Rochette P, Bertrand N, Angers D, Zebarth BJ, Goyer C (2019) Rates and intensity of freeze-thaw cycles affect nitrous oxide and carbon dioxide emissions from agricultural soils. Can J Soil Sci 99:472–484\nRisk N, Snider D, Wagner-Riddle C (2013) Mechanisms leading to enhanced soil nitrous oxide fluxes induced by freeze-thaw cycles. Can J Soil Sci 93:401–414\nSAS Institute I (2013) SAS\u002FACCESS 9.4. Cary, NC, USA\nSims GK, Ellsworth TR, Mulvaney RL (1995) Microscale determination of inorganic nitrogen in water and soil extracts. Commun Soil Sci Plant Anal 26:303–316\nSinger JW, Cambardella CA, Moorman TB (2008) Enhancing nutrient cycling by coupling cover crops with manure injection. Agron J 100:1735–1739\nSong Y, Zou YC, Wang GP, Yu XF (2017) Altered soil carbon and nitrogen cycles due to the freeze-thaw effect: a meta-analysis. Soil Biol Biochem 109:35–49\nTatti E, Goyer C, Chantigny M, Wertz S, Zebarth BJ, Burton DL, Filion M (2014) Influences of over winter conditions on denitrification and nitrous oxide-producing microorganism abundance and structure in an agricultural soil amended with different nitrogen sources. Agric, Ecosyst Environ 183:47–59\nThomas BW, Hao XY, Larney FJ, Goyer C, Chantigny MH, Charles A (2017) Non-legume cover crops can increase non-growing season nitrous oxide emissions. Soil Sci Soc Am J 81:189–199\nWagner-Riddle C, Congreves KA, Abalos D, Berg AA, Brown SE, Ambadan JT, Gao XP, Tenuta M (2017) Globally important nitrous oxide emissions from croplands induced by freeze-thaw cycles. Nat Geosci 10:279–283\nWagner-Riddle C, Furon A, McLaughlin NL, Lee I, Barbeau J, Jayasundara S, Parkin G, Von Bertoldi P, Warland J (2007) Intensive measurement of nitrous oxide emissions from a corn-soybean-wheat rotation under two contrasting management systems over 5 years. Global Change Biol 13:1722–1736\nWagner-Riddle C, Hu QC, van Bochove E, Jayasundara S (2008) Linking nitrous oxide flux during spring thaw to nitrate denitrification in the soil profile. Soil Sci Soc Am J 72:908–916\nWu X, Chen Z, Kiese R, Fu J, Gschwendter S, Schloter M, Liu CY, Butterbach-Bahl K, Wolf B, Dannenmann M (2020) Dinitrogen (N2) pulse emissions during freeze-thaw cycles from montane grassland soil. Biol Fertil Soils 56:959–972\nYang JY, Huffman EC, Drury CF, Yang XM, De Jong R (2011) Estimating the impact of manure nitrogen losses on total nitrogen application on agricultural land in Canada. Can J Soil Sci 91:107–122",{"VOID":1326},"10.1007\u002Fs00374-020-01537-x","http:\u002F\u002Flink.springer.com\u002F10.1007\u002Fs00374-020-01537-x",[1329,1344],{"id":1330,"sortIndex":32,"researcher":28,"roles":1331,"affiliations":1332,"properties":1341},"f0cf63be-86b5-45ae-887c-12b849dbcabd",[1056],[1333],{"id":1334,"sortIndex":32,"affiliation":1335,"properties":28},"1d024352-dffa-4cdc-81ae-5cf81ba07042",{"id":1334,"createTime":28,"updateTime":28,"relativeEntities":1336,"slug":28,"properties":1337,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":1340,"statistic":28},[],{"title":1338},{"VI":1339},"Department of Natural Resource Sciences, Macdonald Campus of McGill University, Ste-Anne-de-Bellevue, Canada",[],{"title":1342},{"VI":1343},"Leanne Ejack",{"id":1345,"sortIndex":40,"researcher":28,"roles":1346,"affiliations":1347,"properties":1354},"e59e6235-4b4c-473a-ae66-e62b294359ce",[1056],[1348],{"id":1334,"sortIndex":32,"affiliation":1349,"properties":28},{"id":1334,"createTime":28,"updateTime":28,"relativeEntities":1350,"slug":28,"properties":1351,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":1353,"statistic":28},[],{"title":1352},{"VI":1339},[],{"title":1355},{"VI":1356},"Joann K. 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a (Medicago sativa, L. cv Aragón) plants were grown under greenhouse conditions in pots of inert sand and vermiculite. The plants were inoculated with Rhizobium meliloti strain 102F28, with Glomus fasciculatus or with a mixture of both microorganisms. Plants inoculated with both Rhizobium and Glomus had the highest shoot dry weight and the lowest root-to-shoot ratio. Roots from dually inoculated plants also had a higher oxygen uptake and nodule nitrogenase activity than those from plants inoculated with either of the two microsymbionts alone. However, the dry weight of the roots from only VAM-infected plants was higher than those from Rhizobium or from Rhizobium plus Glomus-inoculated ones. These differences did not correlate with succinate dehydrogenase activity, which was similar between treatments. Nutrient element concentrations were increased in dually infected plants in comparison with those of plants inoculated with only Rhizobium or Glomus. These data suggest that Rhizobium may affect fungal metabolism and that the effect is not achieved via the tricarboxylic acid pathway.",{"EN":1425},"Possible influence of Rhizobium on VA mycorrhiza metabolic activity in double symbiosis of alfalfa plants (Medicago sativa L.) grown in a pot experiment",{"VOID":1427},"Asai T (1944) Über die Mycorrhizenbildung der Leguminosenpflanzen. Jpn J Bet 13:462–485\nAsimi S, Gianinazzi-Pearson V, Gianinazzi S (1980) Influence of increasing soil phosphorus levels on interaction between vesiculararbuscular mycorrhizae and Rhizobium in soybeans. Can J Bot 58:2200–2205\nAzcón R, Ocampo JA (1981) Factors affecting the vesicular-arbuscular infection and mycorrhizal dependency of thirteen wheat cultivars. N Phytol 87:677–685\nBarea JM, Azcon-Aguilar C (1983) Mycorrhizas and their significance in nodulating nitrogen-fixing plants. Adv Agron 36:1–54\nBedmar EJ, Olivares J (1980) Effect of chemical inhibitors of photorespiration on nitrogenase activity in nodulated alfalfa plants. Planta 150:299–302\nBergersen FJ (1971) Biochemistry of nitrogen fixation in legumes. Annu Rev Plant Physiol 22:121–140\nBethlenfalvay GJ, Brown MS, Pacovsky RS (1982) Parasitic and mutualistic association between a mycorrhizal fungus and soybean: Development of the host plant. Phytopathology 72:889–893\nDel Rio LA, Gómez-Ortega M, Leal A, López-Gorgé J (1977) A more sensitive modification of the catalase assay with the Clark oxygen electrode. J Anal Biochem 80:409–415\nGanry F, Diem HG, Wey J, Dommergues YR (1985) Inoculation with Glomus mosseae improves N2 fixation by field-grown peas. Biol Fertil Soils 1:15–23\nGiovannetti M, Mosse B (1980) An evaluation of techniques for measuring vesicular-arbuscular mycorrhizal infection in roots. N Phytol 84:489–500\nHarley JL, Smith SE (1983) Mycorrhizal symbiosis. Academic Press, London\nHepper CM, O'Shea J (1984) Vesicular-arbuscular mycorrhizal infection in lettuce (Lactuca sativa) in relation to calcium supply. Plant Soil 82:61–68\nKucey RMM, Paul EA (1982) Carbon flow, photosynthesis and N2 fixation in mycorrhizal and nodulated faba beans (Vicia faba L.). Soil Biol Biochem 14:407–412\nMacDonald RM, Lewis M (1978) The occurrence of some acid phosphatases and dehydrogenases in the vesicular-arbuscular mycorrhizal fungus Glomus mosseae. N Phytol 80:135–141\nOcampo JA, Barea JM (1985) Effect of carbamate herbicides on VAM mycorrhizal infection and plant growth. Plant Soil 85:375–383\nPhillips JM, Hayman DS (1970) Improved procedures for clearing and staining parasitic and vesicular-arbuscular mycorrhizal fungi for rapid assessment of infection. Trans Br Mycol Soc 55:158–161\nSmith SE (1982) Inflow of phosphate into mycorrhizal and nonmycorrhizal Trifolium subterraneum at different levels of soil phosphate. N Phytol 90:293–303",{"VOID":1429},"10.1007\u002FBF00257923","http:\u002F\u002Flink.springer.com\u002F10.1007\u002FBF00257923",[1432,1447,1462],{"id":1433,"sortIndex":32,"researcher":28,"roles":1434,"affiliations":1435,"properties":1444},"4233c223-e1df-4b01-bdf3-86453a334f17",[1056],[1436],{"id":1437,"sortIndex":32,"affiliation":1438,"properties":28},"a0a43d3f-3d7b-4d52-a832-8ba63c336935",{"id":1437,"createTime":28,"updateTime":28,"relativeEntities":1439,"slug":28,"properties":1440,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":1443,"statistic":28},[],{"title":1441},{"VI":1442},"Facultad de Agronomía, Universidad Nacional Agraria de la Selva, TingoMaría, Huanaco, Peru",[],{"title":1445},{"VI":1446},"D. 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diversity and activity of disturbed soil in the northern Chihuahuan Desert",{"VOID":1543},"10.1007\u002Fs003740000242",{"EN":1545}," The effects of intense grazing, seasonal drought, and fire on soil microbial diversity (substrate utilization) and activity in a northern Chihuahuan Desert grassland were measured in summer 1997, winter 1998, and spring 1998. Intense livestock grazing was initiated in winter 1995, burning occurred in August 1994, and drought stresses were imposed from October 1994 to June 1997. Microbial diversity was inferred from the carbon substrate utilization patterns in both gram (+) and gram (–) Biolog plates. Microbial activity was estimated by the activity of selected enzymes. Neither microbial diversity nor activity was affected by grazing. The interaction of intense grazing and stress sub-treatments only occurred in spring for one set of diversity measurements. The maximum microbial diversity and activity occurred in the winter-drought-stress sub-plots in summer and spring. Burning reduced microbial diversity and most enzyme activities as compared to the control in summer and spring. Microbial diversity was also lower in summer-drought-stress sub-plots than in the control in summer and spring. Microbial diversity was highest in summer, intermediate in winter, and lowest in spring. Microbial activity was generally higher in summer and lower in winter. It was concluded that substrate availability was the most important factor affecting the diversity and activity of soil microorganisms within a season. Soil moisture was not the factor causing differences in microbial diversity and activity among the stress treatments, but it was a predictor for some microbial responses under a particular stress.","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs003740000242",[1548,1563,1576,1591],{"id":1549,"sortIndex":32,"researcher":28,"roles":1550,"affiliations":1551,"properties":1560},"780feff4-638b-47ed-bea8-72e51691cdec",[1056],[1552],{"id":1553,"sortIndex":32,"affiliation":1554,"properties":28},"c16d84f6-a5c6-4848-b9a7-24f1fd02c087",{"id":1553,"createTime":28,"updateTime":28,"relativeEntities":1555,"slug":28,"properties":1556,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":1559,"statistic":28},[],{"title":1557},{"VI":1558},"Department of Agronomy and Horticulture, New Mexico State University, Box 3Q, Las Cruces, NM 88003, USA e-mail: xliu@nmsu.edu Tel: +1-505-5210864, , MX",[],{"title":1561},{"VI":1562},"X. 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microorganisms associated with the rhizosphere of mangroves in a semiarid coastal lagoon",{"VOID":1673},"10.1007\u002Fs003740050024",{"EN":1675}," The phosphate-solubilizing potential of the rhizosphere microbial community in mangroves was demonstrated when culture media supplemented with insoluble, tribasic calcium phosphate, and incubated with roots of black (Avicennia germinans L.) and white [Laguncularia racemosa (L.) Gaertn.] mangrove became transparent after a few days of incubation. Thirteen phosphate-solubilizing bacterial strains were isolated from the rhizosphere of both species of mangroves: Bacillus amyloliquefaciens, Bacillus licheniformis, Bacillus atrophaeus, Paenibacillus macerans, Vibrio proteolyticus, Xanthobacter agilis, Enterobacter aerogenes, Enterobacter taylorae, Enterobacter asburiae, Kluyvera cryocrescens, Pseudomonas stutzeri, and Chryseomonas luteola. One bacterial isolate could not be identified. The rhizosphere of black mangroves also yielded the fungus Aspergillus niger. The phosphate-solubilizing activity of the isolates was first qualitatively evaluated by the formation of halos (clear zones) around the colonies growing on solid medium containing tribasic calcium phosphate as a sole phosphorus source. Spectrophotometric quantification of phosphate solubilization showed that all bacterial species and A. niger solubilized insoluble phosphate well in a liquid medium, and that V. proteolyticus was the most active solubilizing species among the bacteria. Gas chromatographic analyses of cell-free spent culture medium from the various bacteria demonstrated the presence of 11 identified, and several unidentified, volatile and nonvolatile organic acids. Those most commonly produced by different species were lactic, succinic, isovaleric, isobutyric, and acetic acids. Most of the bacterial species produced more than one organic acid whereas A. niger produced only succinic acid. We propose the production of organic acids by these mangrove rhizosphere microorganisms as a possible mechanism involved in the solubilization of insoluble calcium phosphate.","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs003740050024",[1678,1693,1706,1719,1732],{"id":1679,"sortIndex":32,"researcher":28,"roles":1680,"affiliations":1681,"properties":1690},"b0c7c6b6-23b8-4e1f-a63a-5dbc3b0b1241",[1056],[1682],{"id":1683,"sortIndex":32,"affiliation":1684,"properties":28},"fdc8e581-aa5a-4673-98fc-cd1b08fefbb5",{"id":1683,"createTime":28,"updateTime":28,"relativeEntities":1685,"slug":28,"properties":1686,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":1689,"statistic":28},[],{"title":1687},{"VI":1688},"Environmental Microbiology, The Center for Biological Research of the Northwest (CIB), A.P. 128, La Paz, Baja California Sur 23000, Mexico e-mail: bashan@cibnor.mx Tel: +52-112-53633 ext. 200 Fax: +52-112-54710\u002F53625, , MX",[],{"title":1691},{"VI":1692},"P. 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biologically fixed nitrogen (BNF) by legumes through the 15N natural abundance techniques requires correct determination of a so-called B value. We hypothesized that significant variations in B values exist between faba bean (Vicia faba L.) varieties having consequences for BNF and N balance calculations. We experimentally determined B values for a range of faba bean varieties and quantified to what extent variety has an effect on B values and hence BNF quantification. Seeds of six faba bean varieties released in Ethiopia were inoculated with Rhizobium fabae strain LMG 23997-19 and grown in vermiculite with an N-free nutrient solution in a growth room until full flowering. Total N and 15N content of nodules, roots, and shoot components was analyzed separately to determine the weighted whole plant 15N fractionation during N2 fixation, i.e., the B value. Owing to its large seed size and high N content, a correction for seed N was carried out. We then calculated the percentage of N derived from air (%Ndfa), BNF, and N balance for faba beans grown in the field using three B value scenarios (variety specific B value corrected for seed N, variety specific B value without seed N correction, and a literature derived B value). Whole plant seed N corrected B values were significantly different (P \u003C 0.05) between varieties and varied between +0.5 ± 0.4 and −1.9 ± 1.4‰ suggesting a variable isotope fractionation during N2 fixation. The %Ndfa was significantly (P \u003C 0.05) different between varieties (59 ± 4.2–84 ± 4.5 %) using seed N corrected B values. BNF (218 ± 26.2–362 ± 34.7 kg N ha−1) was significantly (P \u003C 0.05) different between varieties for corrected and uncorrected B values. Soil N balance did not result in statistically significant (P > 0.05) difference between varieties for all three B value scenarios. Use of inappropriate B values masked the difference between varieties and affected their ranking in terms of BNF, resulting from an over- to underestimation of 15 and 19 %, respectively. When applying the 15N natural abundance technique to compare BNF of legume accessions, we recommend determining a B value for each accession. For legumes with large seeds such as faba beans, it is moreover essential to account for seed N when determining the B value.",{"EN":1812},"Importance of correct B value determination to quantify biological N2 fixation and N balances of faba beans (Vicia faba L.) via 15N natural abundance",{"VOID":1814},"Amanuel G, Asefa T, Tanner DG, Mwangi W (1991) On-farm research to derive fertilizer recommendations for small-scale bread wheat production. Methodological issues and technical results. Research report no. 14. IAR, Addis Ababa, Ethiopia\nAmanuel G, Kuhne RF, Tanner DG, Vlek PLG (2000) Biological nitrogen fixation in faba bean (Vicia faba L.) in the Ethiopian highlands as affected by P fertilization and inoculation. Biol Fertil Soils 32:353–359\nBoddey RM, Peoples MB, Palmer B, Dart PJ (2000) Use of the 15N natural abundance technique to quantify biological nitrogen fixation by woody perennials. Nutr Cycl Agroecosyst 57:235–270\nChianu JN, Nkonya EM, Mairura FS, Justina NC, Akinnifesi FK (2011) Biological nitrogen fixation and socioeconomic factors for legume production in sub-Saharan Africa: a review. Agron Sustain Dev 31:139–154\nDawson TE, Mambelli S, Plamboeck AH, Templer PH, Tu KP (2002) Stable isotopes in plant ecology. Annu Rev Ecol Syst 33:507–559\nDoughton JA, Vallis I, Saffigna PG (1992) An indirect method for estimating 15N isotope fractionation during nitrogen fixation by a legume under field conditions. Plant Soil 144:23–29\nFan F, Zhang F, Song Y, Sun J, Bao X, Guo T, Li L (2006) Nitrogen fixation of faba bean (Vicia faba L.) interacting with a non-legume in two contrasting intercropping systems. Plant Soil 283:275–286\nHabtemichial KH, Singh BR, Aune JB (2007) Wheat response to N2 fixed by faba bean (Vicia faba L.) as affected by sulfur fertilization and rhizobial inoculation in semi-arid Northern Ethiopia. J Plant Nutr Soil Sci 170:412–418\nHandley LL, Scrimgeour CM (1997) Terrestrial plant ecology and 15N natural abundance: the present limits to interpretation for uncultivated systems with original data from a Scottish old field. Adv Ecol Res 27:133–212\nHardarson G, Bliss FA, Cigales-Rivero MR, Henson RA, Kipe-Nolt JA, Longeri L et al (1993) Genotypic variation in biological nitrogen fixation by common bean. Plant Soil 152:59–70\nHerridge DF, Peoples M, Boddey RM (2008) Global inputs of biological nitrogen fixation in agricultural systems. Plant Soil 311:1–18\nHögberg P (1997) 15N natural abundante in soil–plant systems. New Phytol 137:179–203\nHögberg P, Näsholm T, Högbom L, Stahl L (1994) Use of 15N labeling and 15N natural abundance to quantify the role of mycorrhizas in N uptake by plants: importance of seed N and of changes in the 15N labeling of the available N. New Phytol 127:515–519\nHoungnandan P, Yemadje RGH, Oikeh O, Djidohokpin CF, Boeckx P, Van Cleemput O (2008) Improved estimation of biological nitrogen fixation of soybean cultivars (Glycine max L. Merril) using 15N natural abundance technique. Biol Fertil Soils 45:175–183\nKöpke U, Nemecek T (2010) Ecological services of faba bean. Field Crop Res 115:217–233\nKyei-Boahen S, Slinkard AE, Walley FL (2002) Isotopic fractionation during N2 fixation by chickpea. Soil Biol Biochem 34:417–420\nLópez-Bellido FJ, López-Bellido RJ, Redondo R, López-Bellido L (2010) B value and isotopic fractionation in N2 fixation by chickpea (Cicer arietinum L.) and faba bean (Vicia faba L.). Plant Soil 337:425–434\nMaidl FX, Haunz FX, Panse A, Fischbeck G (1996) Transfer of grain legume nitrogen within a crop rotation containing winter wheat and winter barley. J Agron Crop Sci 176:47–57\nNebiyu A, Diels J, Boeckx P (2010) Performance of elite faba bean (Vicia faba L.) varieties at two different altitudes on Nitisols of southwestern Ethiopia. Soil Science Society of Belgium, 23 February 2010, Brussels, Belgium. http:\u002F\u002Fwww.bbvbss.ugent.be\u002Fdownloads\u002Fyss2010\u002Famsalu.pdf\nNguluu SN, Probert ME, McCown RL, Myers RJK, Waring SA (2001) Isotopic discrimination associated with symbiotic nitrogen fixation in stylo (Stylosanthes hamata L.) and cowpea (Vigna unguiculata L.). Nutr Cycl Agroecosyst 62:11–14\nNorris DO, Date RA (1976) Legume bacteriology. In: Shaw NH and Bryan WW (eds.) Tropical pasture research—principles and methods. Commonwealth Bureau and Pastures and Field Crops Bulletin No. 51, Oxford, pp. 171-174\nOkito A, Alves BRJ, Urquiaga S, Boddey RM (2004) Isotopic fractionation during N2 fixation by four tropical legumes. Soil Biol Biochem 36:1179–1190\nPate JS, Unkovich MJ, Armstrong EL, Sanford P (1994) Selection of reference plants for 15N natural abundance assessment of N2 fixation by crop and pasture legumes in south-west Australia. Aust J Agric Res 45:133–147\nPeoples MB, Turner GL, Shah Z, Shah SH, Aslam M, Ali S, Markey SL, Afandi F, Schwenke GD, Herridge DF (1997) Evaluation of the 15N natural abundance technique for measuring N2 fixation in experimental plots and farmer’s fields. In: Rupela OP, Johansen C, Herridge DF (eds) Extending nitrogen fixation research to farmers’ fields. ICRISAT, Patancheru, India, pp 57–75\nPeoples MB, Brockwell J, Herridge DF, Rochester I, Alves B, Boddey R, Dakora F, Bhattari S, Maskey S, Sampet C, Rerkesam B, Khan D, Hauggaard-Nielsen H, Jensen E (2009a) The contribution of nitrogen fixing crop legumes to the productivity of agricultural systems. Symbiosis 48:1–17\nPeoples MB, Unkovich MJ, Herridge DF (2009b) Measuring symbiotic nitrogen fixation by legumes. In: David W, Emerich DW, Krishnan HB (eds) Nitrogen fixation in crop production. Agronomy Monograph 52. American Society of Agronomy, Madison, pp 125–170\nRobinson D, Handley LL, Scrimgeour CM (1998) A theory for 15N\u002F14N fractionation in nitrate-grown vascular plants. Planta 205:397–406\nRodriguez-Navarro DN, Buendia AM, Camacho M, Lucas MM, Santamaria C (2000) Characterization of Rhizobium spp. bean isolates from south-west Spain. Soil Biol Biochem 32:1601–1613\nSalvagiotti F, Cassman K, Specht J, Walters D, Weiss A, Dobermann A (2008) Nitrogen uptake, fixation and response to fertilizer N in soybeans: a review. Field Crop Res 108:1–13\nSAS (Statistical Analysis System) (2008) SAS\u002FSTAT 9.2 user’s guide. SAS institute Inc, Cary\nShearer G, Kohl DH (1986) N2-fixation in field settings: estimations based on natural 15N abundance. Funct Plant Biol 13:699–756\nShearer G, Kohl DH (1988) Natural 15N abundance as a method of estimating the contribution of biologically fixed nitrogen to N2 fixing systems: potential for non-legumes. Plant Soil 110:317–327\nUnkovich MJ, Pate JS (2000) An appraisal of recent field measurements of symbiotic N2 fixation by annual legumes. Field Crop Res 65:211–228\nUnkovich MJ, Pate JS, Armstrong EL (1994) Potential precision of the δ15N natural abundance method in field estimated of nitrogen fixation by crop and pasture legumes in south-west Australia. Aust J Agric Res 45:119–132\nUnkovich MJ, Herridge D, Peoples M, Cadisch G, Boddey R, Giller K, Alves B, Chalk P (2008) Measuring plant-associated nitrogen fixation in agricultural systems. ACIAR Monograph No. 136, 258 pp\nUnkovich MJ, Baldock J, Peoples MB (2010) Prospects and problems of simple linear models for estimating symbiotic N2 fixation by crop and pasture legumes. Plant Soil 329:75–89\nVincent JM (1970) A manual for the practical study of root nodule bacteria. Blackwell Scientific, Oxford, p 164\nWanek W, Arndt SK (2002) Differences in delta15N signatures between nodulated roots and shoots of soybean is indicative of the contribution of symbiotic N2 fixation to the plant. 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pot experiment was conducted to investigate the influences of indigenous phototrophs on methane (CH4) emissions from a paddy soil where rice straw was incorporated or was surface-applied. During the cultivation, half of the pots were covered with aluminum foil, except for the minimum space for rice plants, to prevent ambient light reaching the floodwater or the soil surface. Growth of oxygen-producing phototrophs was hardly observed in the unilluminated plots, whereas intensive growth of algae, duckweed and hydrophytes was found in the illuminated ones. Plant growth was not affected by the different treatments. Seasonal changes in CH4 emission determined by a closed chamber method indicated that illumination had no or only minor effects on CH4 emissions when rice straw was incorporated or was not applied, but significantly reduced CH4 emissions when rice straw was surface-applied. Methanogenesis occurring in the soil-floodwater interface was further investigated in two lab-scale model experiments measuring methanogenic activity. As a result, more activated methanogenesis was found in the surface-applied rice straw and the soil around the straw compared with the soil incubated without rice straw. The magnitude of the methanogenic activity in the rice straw incubated under illuminated conditions was significantly lower than that incubated in the dark. Consequently, this study demonstrates that methanogenesis in paddy soil occurs even in the soil-floodwater interface if plant residues like rice straw exist, and such methanogenesis is likely to be suppressed by growth of indigenous phototrophs under illumination.",{"EN":1958},"Influences of indigenous phototrophs on methane emissions from a straw-amended paddy soil",{"VOID":1960},"Aulakh MS, Wassmann R, Rennenberg H (2000) Methane emissions from rice fields—quantification, mechanisms, role of management, and mitigation options. Adv Agron 70:193–260\nBharati K, Mohanty SR, Singh DP, Rao VR, Adhya TK (2000) Influence of incorporation or dual cropping of Azolla on methane emission from a flooded alluvial soil planted to rice in eastern India. Agric Ecosyst Environ 79:73–83\nBont JAM de, Lee KK, Bouldin DF (1978) Bacterial oxidation of methane in rice paddy. Ecol Bull 26:91–96\nBossio DA, Horwath WR, Mutters RG, van Kessel C (1999) Methane pool and flux dynamics in a rice field following straw incorporation. Soil Biol Biochem 31:1313–1322\nChareonsilp N, Buddhaboon C, Promnart P, Wassmann R, Lantin RS (2000) Methane emission from deepwater rice fields in Thailand. Nutr Cycl Agroecosyst 58:121–130\nCheng W, Chander K, Inubushi K (2000) Effect of elevated CO2 and temperature on methane production and emission from submerged soil microcosms. Nutr Cycl Agroecosyst 58:339–347\nClément B, Merlin G (1995) The contribution of ammonia and alkalinity to landfill leachate toxicity to duckweed. Sci Total Environ 170:71–79\nDannenberg S, Conrad R (1999) Effect of rice plants on methane production and rhizospheric metabolism in paddy soil. Biogeochemistry 45:53–71\nGilbert B, Frenzel P (1995) Methanotrophic bacteria in the rhizosphere of rice microcosms and their effect on porewater methane concentration and methane emission. Biol Fertil Soils 20:93–100\nHanaki M, Ito T, Saigusa M (2002) Effect of no-tillage rice (Oryza sativa L.) cultivation on methane emission in three paddy fields of different soil types with rice straw application. Jpn J Soil Sci Plant Nutr 73:135–143\nHarada N, Nishiyama M, Matsumoto S (2001) Inhibition of methanogens increases photo-dependent nitrogenase activities in anoxic paddy soil amended with rice straw. FEMS Microbiol Ecol 35:231–238\nHolzapfel-Pschorn A, Seiler W (1986) Methane emission during a cultivation period from an Italian rice paddy. J Geophys Res 91:11803–11814\nInubushi K, Hori K, Matsumoto S, Umebayashi M, Wada H (1989) Methane emission from the flooded paddy soil to the atmosphere through rice plant. Jpn J Soil Sci Plant Nutr 60:318–324\nInubushi K, Hori K, Matsumoto S, Wada H (1997) Anaerobic decomposition of organic carbon in paddy soil in relation to methane emission to the atmosphere. Water Sci Tech 36:523–530\nKaku N, Ueki A, Ueki K (1999) Sample preparation for methanogenic activities of heterogeneous flooded rice soils. Microb Environ 14:151–156\nKimura M, Asai K, Watanabe A, Murase J, Kuwatsuka S (1992) Suppression of methane fluxes from flooded paddy soil with rice plants by foliar spray of nitrogen fertilizers. Soil Sci Plant Nutr 38:735–740\nKing GM (1990) Regulation by light of methane emission from a wetland. Nature 345:513–515\nLadha JK, Tirol-Padre A, Daroy MLG, Punzalan G, Watanabe I (1987) The effects on N2 fixation (C2H2 reduction), bacterial population and rice plant growth of two modes of straw application to a wetland rice field. Biol Fertil Soils 5:106–111\nLampe K (1995) Rice research: food for 4 billion people. GeoJournal 35:253–259\nMatsuguchi T, Yoo ID (1981) Stimulation of phototrophic N2 fixation in paddy fields through rice straw application. In: Wetselaar R, Simpson JR, Rosswall T (eds) Nitrogen cycling in Southeast Asian wet monsoonal ecosystems. Australian Academy of Science, Canberra, pp 18–25\nMinoda T, Kimura M (1996) Photosynthates as dominant source of CH4 and CO2 in soil water and CH4 emitted to the atmosphere from paddy fields. J Geophys Res 101:21091–21097\nMiura Y, Watanabe A, Kimura M, Kuwatsuka S (1992) Methane emission from paddy field. Part 2. Main route of methane transfer through rice plant, and temperature and light effects on diurnal variation of methane emission. Environ Sci 5:187–193\nMosier AR (1998) Soil processes and global warming. Biol Fertil Soils 27:221–229\nMowjood MIM, Kasubuchi T (1998) Dynamics of dissolved oxygen (DO) in ponded water of a paddy field. Soil Sci Plant Nutr 44:405–413\nNouchi I, Mariko S, Aoki K (1990) Mechanism of methane transport from the rhizosphere to the atmosphere through rice plants. Plant Physiol 94:59–66\nPfennig N, Trüper HG (1989) Section 18. Anoxygenic phototrophic bacteria. In: Staley JT, Bryant MP, Pfennig N, Holt JG (eds) Bergey’s manual of systematic bacteriology, vol 3. Williams & Wilkins, Baltimore, pp 1635–1709\nPonnamperuma FN (1972) The chemistry of submerged soils. Adv Agron 24:29–96\nSass RL, Fisher FM (1997) Methane emissions from rice paddies: a process study summary. Nutr Cycl Agroecosyst 49:119–127\nSass RL, Fisher FM, Harcombe PA, Turner FT (1991a) Mitigation of methane emissions from rice fields: possible adverse effects of incorporated rice straw. Global Biogeochem Cycl 5:275–287\nSass RL, Fisher FM, Turner FT, Jund MF (1991b) Methane emission from rice fields as influenced by solar radiation, temperature, and straw incorporation. Global Biogeochem Cycl 5:335–350\nTakai Y, Kamura T (1966) The mechanism of reduction in waterlogged paddy soil. Folia Microbiol 11:304–313\nUeki A, Nishida S, Kumakura M, Kaku N, Kainuma Y, Hattori C, Fujii H, Ueki K (1999) Effects of organic matter application, temperature, and sunshine duration on seasonal and annual variations of methanogenic activity in wetland rice field soil. Soil Sci Plant Nutr 45:811–823\nWang WC (1991) Ammonia toxicity to macrophytes (common duckweed and rice) using static and renewal methods. Environ Toxicol Chem 10:1173–1177\nWassmann R, Neue HU, Alberto MCR, Lantin RS, Bueno C, Llenaresas D, Arah JRM, Papen H, Seiler W, Rennenberg H (1996) Fluxes and pools of methane in wetland rice soils with varying organic inputs. Environ Monit Assess 42:163–173\nWatanabe I, Hashimoto T, Shimoyama A (1997) Methane-oxidizing activities and methanotrophic populations associated with wetland rice plants. Biol Fertil Soils 24:261–265\nYagi K, Minami K (1990) Effect of organic matter application on methane emission from some Japanese paddy fields. Soil Sci Plant Nutr 36:599–610\nYagi K, Tsuruta H, Minami K (1997) Possible options for mitigating methane emission from rice cultivation. Nutr Cycl Agroecosyst 49:213–220\nYang SS, Chang HL (1998) Effect of environmental conditions on methane production and emission from paddy soil. Agric Ecosyst Environ 69:69–80\nYoo ID, Kimura M, Wada H, Takai Y (1984) Effects of application of different rice straw on biological N2-fixation in paddy soils. Jpn J Soil Sci Plant Nutr 55:455–459\nYoo ID, Kimura M, Wada H, Takai Y (1990) The release of organic and inorganic nutrients from soils surface-applied with rice straw and its contribution to biological N2-fixation. 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studies on the decomposition of straw using the mesh bag technique were carried out under field conditions in south Estonia. Straw of spring and winter cereals (Hordeum vulgare L., Secale cereale L., Triticum aestivum L.) was compared over different periods and at two depths (5 and 20 cm). Calculation of straw decomposition was based on the ash-free organic matter weight loss. Depending on experimental and climatic conditions the decomposition rate fluctuated from 42% to 75% during the 1st year. The three experimental factors incorporation period, incorporation depth and straw species all had a significant effect on the decomposition of straw. The decaying processes proceeded more rapidly in the upper layer and during the initial months; later there were no differences in decomposition rate between the two depths. During the period without vegetation, i.e. from freezing (December) to thawing (April) of the soil, the decomposition rate was 6–7% and during autumn it was about 10%. Greater loss of straw occurred early in the growing season and in the upper layer. The release of nitrogen from straw was slow and N quantity in straw increased due to microbiological immobilization during the 1st year.",{"EN":2097},"Effect of incorporation depth and soil climate on straw decomposition rate in a loamy Podzoluvisol",{"VOID":2099},"Anderson RV, Elliot ET, McClellan FJ, Coleman DC, Cole CV, Hunt HW (1978) Trophic interactions in soils as they affect energy and nutrient dynamics. III Biotic interactions of bacteria, amoebae, and nematodes. Microb Ecol 4:361–371\nBerg B, Hannus K, Popoll T, Theander O (1982) Changes in organic-chemical components during litter decomposition. Long term decomposition in a Scots pine forest. Can J Bot 60:1310–1319\nBoguslawski E von (1964) Die Verwertung der Strohernten als Strohdüngung. Arb DLG 96\nBottner P (1985) Response of microbial biomass to alternate moist and dry conditions in a soil incubated with 14C-and 15N-labelled plant material. Soil Biol Biochem 6:329–337\nCampbell CA, Biederbeck VO, Warder FO, Robertson GW (1973) Effect of rainfall and subsequent drying on nitrogen and phosphorus changes in a dryland fallow loam. Soil Sci Soc Am Proc 37:909–915\nCannell RQ (1984) Straw incorporation in relation to soil conditions and crop growth. Outl Agric 13:130–135\nCheshire MV, Griffiths BS (1989) The influence of earthworms and cranefly larvae on the decomposition of uniformly 14C labelled plant material in soil. J Soil Sci 40:117–124\nCochran VL (1991) Decomposition of barley straw in a subarctic soil in the field. Biol Fertil Soils 10:227–232\nCochran VL, Elliot LF, Lewis CE (1989) Soil microbial biomass and enzyme activity in subarctic agricultural and forest soils. Biol Fertil Soils 7:283–288\nCollins HP, Elliot LF, Papendick R (1990) Wheat straw decomposition and changes in decomposability during filed exposure. Soil Sci Soc Am J 54:1013–1016\nChristensen BT (1985) Wheat and barley straw decomposition under field conditions: effect of soil type and plant cover on weight loss, nitrogen and potassium content. Soil Biol Biochem 17:691–697\nChristensen BT (1986) Barley straw decomposition under field conditions: effect of placement and initial nitrogen content on weight loss and nitrogen dynamics. Soil Biol Biochem 18: 523–529\nDouglas CL, Allmaras Jr R, Rasmussen PE, Ramig RE, Roager NC (1980) Wheat straw composition and placement effects on decomposition in dryland agriculture of the Pacific Northwest. Soil Sci Soc Am J 44:833–837\nFollet RH, Gupta SC, Hunt PG (1987) Conservation practice: relation to the mangement of crop production. In: Mordvedt JJ, Buxton DR (eds) Soil fertility and organic matter as critical component of production systems. Soil Sci Soc Am Spec Publ 19:19–51\nFranko U (1986) Die Mineralisierung der organischen Substanz im Boden außerhalb der Vegetationsperiode. Arch Acker-und Pflanzenbau und Bodenkd 7:391–394\nGoering HK, Soest PF van (1970) Forage fiber analyses. Apparatus, reagents, procedures, and some applications. Agric Handbook No. 379. Agric Res Service, USDA\nHammouda GH, Adams WA (1987) The decomposition, huminification and fate of nitrogen during the composting of some plant residues. Compost Prod Qual and Use. Proc Symp Udine, 17–19 Apr 1986. London, New York, pp 245–253\nHarper SHT, Lynch JM (1981b) The kinetics of straw decomposition in relation to its potential to produce the phytotoxin acetic acid. J Soil Sci 32:627–637\nJawson MD, Eliot LF, Papendick RI, Campell GS (1989) The decomposition of 14C-labelled wheat straw and 15-N labelled microbial material. Soil Biol Biochem 21:417–422\nJensen MB (1985) Interactions between soil invertebrates and straw in soil. Pedobiologia 28:59–69\nKirchmann H (1985) Losses, plant uptake and utilization of manure nitrogen during a production cycle. Acta Agric Scand [Suppl] 24:1–77\nLadd JN, Oades JM, Amato M (1981) Microbial biomass formed from 14C, 15N-labelled plant material decomposing in soils in the field. Soil Biol Biochem 13:417–425\nMagan N, Hand P, Kirkwood IA, Lynch JM (1989) Establishment of microbial inoculation on decomposing wheat straw in soil of different water contents. Soil Biol Biochem 1:15–22\nMartin JP, Haider K (1986) Influence of mineral colloids on turnover rates of soil organic carbon. In: Huang PM, Schnitzer M (eds) Interactions of soil minerals with natural organic and microbes. Soil Sci Soc Am Spec Publ 17:284–304\nMartiniuk S, Wagner GH (1978) Quantitative examination of soil microflora associated with different management systems. Soil Sci 125:343–350\nMarumoto T, Anderson JPE, Domsch KH (1982) Decomposition of 14C- and 15N-labelled microbial cells in soil. Soil Biol Biochem 14:461–467\nMurayama S (1984) Decomposition kinetics of straw saccharide and synthesis of microbial saccharide under field conditions. J Soil Sci 35:231–242\nParker DT, Larson WE, Bartholomew WV (1957) Studies on nitrogen tie-up as influenced by location of plant residues in soils. Soil Sci Soc Am Proc 21:608–612\nPowlson DS, Jenkinson DS, Pruden G, Johnston AE (1985) The effect of straw incorporation on the uptake of nitrogen by winter wheat. J Sci Food Agric 36:26–30\nSchröder A, Gewehr B (1977) Stroh-und Zelluloseabbau in verschiedenen Bodentypen. Z Pflanzenernaehr Bodenkd 140: 273–284\nSmith JH, Peckenpaugh RE (1986) Straw decomposition in irrigated soil. Comparison of twenty-three cereal straws. Soil Sci Soc Am J 50:928–932\nSparling GP, Chesire MV, Mundie CM (1982) Effect of barley palnts on the decomposition of 14C-labelled soil organic matter. J Soil Sci 33:89–100\nStott DE, Stroo HF, Elliot Lf, Papendick RI, Campell GS (1986) Low temperature or low water potential effects on the microbial decomposition of wheat residue. Soil Biol Biochem 18: 577–582\nStott DE, Stroo HF, Elliot LF, Papendick RI, Unger PW (1990) Wheat residue loss from fields under no-till management. Soil Sci Soc Amer J 54:92–98\nSummerell BA, Burgess LW (1989) Decomposition and chemical composition of cereal straw. Soil Biol Biochem 21:551–559\nSörensen LN (1974) Rate of decomposition of organic matter in soil as influenced by repeated air drying-rewetting and repeated additions of organic material. Soil Biol Biochem 6:287–292\nTamm E, Krzysch G (1966) The intensity of the breakdown of organic manures during the winter half-year. Z Acker-Pflanzenbau 2:101–111\nTikhonov AV (1980) Dynamics of decomposition of different varieties in soil (in Russian). Moscow, J Agrochem 6:59–63\nVanagas I (1983) Effect of organic fertilizers and pesticides on changes in soil organisms and nutritive regime (in Russian). Thesis Ph D degree, Kaunas, p 16\nVan Veen JA, McGill WB, Hunt HW, Frissel MJ, Cole CV (1981) Simulation models of the terrestrial nitrogen cycle. In: Clark FE, Roswall T (eds) Terrestrial nitrogen cycle. Processes, ecosystems, strategies and management impacts. Ecol Bull (Stockholm) 33:25–48\nVoroney RP, Paul EA, Anderson DW (1989) Decomposition of wheat straw and stabilization of microbial products. Can J Soil Sci 69:63–77\nWagger MG, Kissel DE, Smith SJ (1985) Mineralization of nitrogen from nitrogen-15 labelled crop residues under field conditions. Soil Sci Soc Am J 49:1220–1226\nWessen B, Berg B (1986) Long-term decomposition of barley straw. Chemical changes and growth of fungal mycelium. Soil Biol Biochem 18:55–59\nZabolotskaya TG, Lyutoeva MN (1974) After harvest remains of field crops, their composition and effect on content of mobile forms of nitrogen in some podzolic soils (in Russian). Moscow J Agrochem 2:3–8\nZiegler F, Zech W (1991) Veranderungen in der stofflichen Zusammensetzung von Buchenstreu und Gerstenstroh beim Abbau unter Laborbedingungen. Z Pflanzenernaehr Bodenkd 154: 377–385",{"VOID":2101},"10.1007\u002FBF00336557","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002FBF00336557",[2104],{"id":2105,"sortIndex":32,"researcher":28,"roles":2106,"affiliations":2107,"properties":2116},"b92dfc7b-62b4-4c35-a59a-268d072578ff",[1056],[2108],{"id":2109,"sortIndex":32,"affiliation":2110,"properties":28},"0f525172-3b35-4b90-8235-bc2d9c4525b5",{"id":2109,"createTime":28,"updateTime":28,"relativeEntities":2111,"slug":28,"properties":2112,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":2115,"statistic":28},[],{"title":2113},{"VI":2114},"Department of Soil Science, Estonian Agricultural University, Eerika, Tartu, Estonia",[],{"title":2117},{"VI":2118},"A Kanal",{"url":2102,"publisher":2120,"properties":2169},{"id":868,"createTime":869,"updateTime":870,"relativeEntities":2121,"slug":872,"properties":2122,"entityType":25,"verifyStatus":878,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":32,"subjectFields":2125,"manageAffiliations":2138,"indexDatabases":2149,"url":28,"thumbnailPath":28,"statistic":2164,"gsStatistic":28,"type":55,"analyzePriority":28},[],{"issn":2123,"title":2124},{"VOID":875},{"EN":877},[2126,2130,2134],{"id":881,"createTime":28,"updateTime":28,"relativeEntities":2127,"label":2128,"description":2129,"parentId":28,"standard":28,"scholarHubFieldId":28},[],{"EN":884},{},{"id":887,"createTime":28,"updateTime":28,"relativeEntities":2131,"label":2132,"description":2133,"parentId":28,"standard":28,"scholarHubFieldId":28},[],{"EN":890},{},{"id":893,"createTime":28,"updateTime":28,"relativeEntities":2135,"label":2136,"description":2137,"parentId":28,"standard":28,"scholarHubFieldId":28},[],{"EN":896},{},[2139,2144],{"id":900,"createTime":28,"updateTime":28,"relativeEntities":2140,"slug":28,"properties":2141,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":2143,"statistic":28},[],{"title":2142},{"EN":904},[],{"id":907,"createTime":28,"updateTime":28,"relativeEntities":2145,"slug":28,"properties":2146,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":2148,"statistic":28},[],{"title":2147},{"EN":911},[913],[2150,2157],{"id":916,"indexDatabase":2151,"url":928,"indexYears":28,"academicFieldIds":2156,"indexDatabaseRanking":28},{"id":918,"createTime":28,"updateTime":28,"relativeEntities":2152,"label":2153,"description":2154,"key":925,"publicationTags":2155,"standard":28},[],{"EN":921,"VI":921},{"EN":923,"VI":924},[927,813],[930],{"id":932,"indexDatabase":2158,"url":938,"indexYears":939,"academicFieldIds":2163,"indexDatabaseRanking":944},{"id":775,"createTime":28,"updateTime":28,"relativeEntities":2159,"label":2160,"description":2161,"key":781,"publicationTags":2162,"standard":28},[],{"EN":778,"VI":778},{"EN":778,"VI":780},[783],[941,942,943],{"impactFactor":32,"impactFactorByYear":2165,"i10Index":41,"i10IndexLast5Year":132,"totalPublication":951,"totalPublicationByYear":2166,"totalCitation":957,"totalCitationByYear":2167,"totalCitationPerPublication":993,"totalCitationPerPublicationByYear":2168,"hindexLast5Year":354,"hindex":354},{"2012":369,"2013":947,"2014":948,"2015":820,"2016":367,"2017":821,"2018":949,"2019":823,"2020":950,"2021":948,"2022":948,"2023":341},{"1985":130,"1986":131,"1987":530,"1988":158,"1989":151,"1990":560,"1991":156,"1992":611,"1993":599,"1994":156,"1995":826,"1996":953,"1997":154,"1998":428,"1999":954,"2000":955,"2001":954,"2002":358,"2003":690,"2004":956,"2005":560,"2006":151,"2007":600,"2008":151,"2009":207,"2010":208,"2011":611,"2012":566,"2013":565,"2014":688,"2015":161,"2016":157,"2017":160,"2018":279,"2019":434,"2020":156,"2021":516,"2022":325,"2023":160,"2024":135},{"1985":959,"1986":131,"1987":960,"1988":961,"1989":962,"1990":963,"1991":38,"1992":964,"1993":965,"1994":966,"1995":967,"1996":968,"1997":969,"1998":970,"1999":971,"2000":972,"2001":973,"2002":621,"2003":974,"2004":975,"2005":976,"2006":977,"2007":978,"2008":979,"2009":977,"2010":980,"2011":981,"2012":982,"2013":983,"2014":984,"2015":985,"2016":986,"2017":987,"2018":988,"2019":989,"2020":990,"2021":991,"2022":992,"2023":145,"2024":45},{"1985":995,"1986":40,"1987":996,"1988":997,"1989":998,"1990":999,"1991":1000,"1992":1001,"1993":1002,"1994":1003,"1995":1004,"1996":1005,"1997":1006,"1998":1007,"1999":1008,"2000":1009,"2001":1010,"2002":1011,"2003":1012,"2004":1013,"2005":1014,"2006":1015,"2007":1016,"2008":1017,"2009":1018,"2010":1019,"2011":1020,"2012":131,"2013":1021,"2014":1022,"2015":1023,"2016":1024,"2017":1025,"2018":1026,"2019":637,"2020":1027,"2021":1028,"2022":1029,"2023":109,"2024":681},{"pages":2170,"volume":2172},{"VOID":2171},"190-196",{"VOID":2173},"20","1995-08-01",1995,[927,944],{"id":2178,"createTime":2179,"updateTime":2179,"relativeEntities":2180,"slug":28,"properties":2181,"entityType":1049,"verifyStatus":878,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":32,"primaryUrl":2188,"fullTextUrl":28,"authors":2189,"publicationType":1082,"publisherRelationship":2233,"citationCount":28,"citationInfo":28,"publishDate":1800,"publishYear":982,"citationAnalyzeStatus":878,"lastCitationAnalyze":28,"indexDatabases":2287,"openAccess":28,"references":28,"isForceReanalyzing":1141},"010d36c0-36b5-43dc-b704-94f227c58c93","2023-12-28T10:44:20.992+00:00",[],{"title":2182,"doi":2184,"abstract":2186},{"EN":2183},"Rhizobiology and nitrogen fixation of some tree legumes native to Sri Lanka",{"VOID":2185},"10.1007\u002Fs003740050033",{"EN":2187}," Rhizobiology of four tree legumes, Abarema bigemina (endemic), Adenanthera bicolor (endemic), Humboldtia laurifolia (indigenous) and Pericopsis mooniana (indigenous), was studied by: (1) observations of their in situ root nodulation, (2) characterization and authentication of rhizobia isolated from them, and (3) an examination of the infectivity and effectivity of the rhizobial isolates using the respective hosts and the broad-spectrum host, siratro (Macroptillium atropurpureum). Investigations were also conducted to evaluate the effect of rhizobial inoculation on growth and N fixation of the valuable timber species, P. mooniana, during its early stages of growth. All the hosts revealed in situ nodulation, except A. bicolor which had nodule-like swellings on its roots. While four rhizobial isolates were obtained from A. bigemina, four from H. laurifolia and 18 from P. mooniana, no authentic rhizobia were isolated from A. bicolor. The nodule-like structures did not show acetylene reduction activity, and the plants failed to nodulate upon inoculation with rhizosphere soil. A. bicolor was therefore tentatively assigned as a non-nodulating species. This report includes the first description of root nodules in the endemic species A. bigemina and the indigenous species H. laurifolia and the isolation and characterization of rhizobia from them. Significant differences were observed among the isolates with regard to their infectivity and effectivity. One isolate from P. mooniana was outstanding in its infectivity and effectivity on the original host, as well as on siratro. Inoculation of P. mooniana with this isolate together with a reference strain significantly improved nodulation and N fixation and gave a 50% increase in plant dry matter under a low level of N fertilizer, during a 12-month growth period. It is suggested that the nursery culture of P. mooniana could be improved by inoculation under low N-input conditions. The ability of these rhizobia to persist in the soil for a 12-month period was observed by the use of strains marked with antibiotics.","https:\u002F\u002Flink.springer.com\u002Farticle\u002F10.1007\u002Fs003740050033",[2190,2205,2218],{"id":2191,"sortIndex":32,"researcher":28,"roles":2192,"affiliations":2193,"properties":2202},"b2e54b7f-1e21-430b-8f8f-735ea3eefa0e",[1056],[2194],{"id":2195,"sortIndex":32,"affiliation":2196,"properties":28},"04d331e3-47f2-4986-8449-d0a295cd7e2b",{"id":2195,"createTime":28,"updateTime":28,"relativeEntities":2197,"slug":28,"properties":2198,"entityType":28,"verifyStatus":28,"verifyTime":28,"verifyNote":28,"languages":28,"translateLanguages":28,"viewCount":28,"url":28,"parentIds":2201,"statistic":28},[],{"title":2199},{"VI":2200},"Sri Lanka-Belgium Project on Biological Nitrogen Fixation, Institute of Fundamental Studies, Hantana Road, Kandy, Sri Lanka, , LK",[],{"title":2203},{"VI":2204},"T.I. 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