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1

Noss, R. F. « Sustaining Ecological Integrity ». Global Bioethics 14, no 1 (janvier 2001) : 11–20. http://dx.doi.org/10.1080/11287462.2001.10800775.

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Miller, Julie Ann. « Biosciences and Ecological Integrity ». BioScience 41, no 4 (avril 1991) : 206–10. http://dx.doi.org/10.2307/1311408.

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Warren Heiti. « Lyric Details and Ecological Integrity ». Ethics and the Environment 22, no 1 (2017) : 89. http://dx.doi.org/10.2979/ethicsenviro.22.1.05.

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Ordóñez, Camilo, et Peter N. Duinker. « Ecological integrity in urban forests ». Urban Ecosystems 15, no 4 (4 mai 2012) : 863–77. http://dx.doi.org/10.1007/s11252-012-0235-6.

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Cairns, John. « Ecological integrity of aquatic systems ». Regulated Rivers : Research & ; Management 11, no 3-4 (novembre 1995) : 313–23. http://dx.doi.org/10.1002/rrr.3450110307.

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Erba, Valeria, et Mina di Marino. « Reti ecologiche : pianificazione e progetti territoriali ». TERRITORIO, no 58 (septembre 2011) : 17–26. http://dx.doi.org/10.3280/tr2011-058003.

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Il tema delle reti ecologiche in questo contributo di riflessione scientifica e di sperimentazione didattica viene utilizzato per i possibili sviluppi futuri di approccio sostenibile, integrato e multidisciplinare con la pianificazione territoriale, la progettazione urbanistica e architettonica. Il paradigma di sostenibilitŕ ambientale e sociale delle reti ecologiche sia a livello programmatico-strategico che progettuale, viene applicato all'elaborazione dei tre progetti ricadenti nelle province lombarde di Varese, Lecco e Como. Le sperimentazioni non si limitano a un progetto tradizionale di rete ecologica finalizzato solo alla conservazione della biodiversitŕ (a scala regionale, provinciale e locale), ma all'impiego del medesimo strumento concettuale integrato alle componenti urbanistiche e territoriali per valutare, regolare e/o progettare trasformazioni territoriali sostenibili.
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Vidal, Laura, Adriana Vallarino, Ileana Benítez et Jorge Correa. « Implementation of the Ramsar strategic plan in coastal wetlands of the Península de Yucatán : regulations and normativity ». Latin American Journal of Aquatic Research 43, no 5 (28 février 2017) : 873–87. http://dx.doi.org/10.3856/vol43-issue5-fulltext-7.

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The way how Mexico applies the normative and other management strategies, regarding coastal wetland and wetlands birds conservation of the Península de Yucatán following the Ramsar Strategic Plan 2009- 2015 is analyzed. Regulatory criteria within Management Programs of Natural Protected Areas and Ecologic Ordinance Instruments were analyzed identifying strengths and weaknesses under an ecological integrity concept. Results show the need to homogenize the concept of integrity within regulation, to develop a hierarchical spatial structure for management strategies. It will: a) promotes connectivity, b) strength the perception of buffer zones and critical habitats, c) emphasize in the protection of biologic heterogeneity in space and time, ecological processes and trophic networks and, develop regulation about wetland restoration. We conclude that current normative framework is still very inefficient and a systemic vision is required to protect these ecosystems. Nine suggestions to improve the current scenario are included.
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Robinson, Jennifer M. « Global change and regional integrity ». Ecological Modelling 75-76 (septembre 1994) : 213–20. http://dx.doi.org/10.1016/0304-3800(94)90020-5.

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Singh, Rajbeer, Prakash Nautiyal et Rachana Nautiyal. « Evaluation of the ecological state of the major streams located in Doon valley using diatoms as indicators ». Journal of Applied and Natural Science 10, no 1 (1 mars 2018) : 500–506. http://dx.doi.org/10.31018/jans.v10i1.1658.

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Biological communities reflect overall ecological integrity (i.e. chemical, physical and biological integrity). Since the diatom species exhibit variation in tolerances to physical and chemical change in water, they are excellent indicators changes in their environment. Based on the dominant categories for each characteristic, the ecological state of the stream can be determined. This study evaluates the ecological state of the streams in Doon Valley. The diatom samples collected at regular monthly intervals from the twelve streams located in the eastern and western Doon were treated with acid-peroxide and mounted in Naphrax for species count at x1500. About 250-300 valves of diatom species were counted and Van Dam ecologic values were computed by OMNIDIA ver. 5.3. pH was alkaliphilous (4), salinity - fresh brackish (2) and oxygenation - continuously high (1) for most of the streams. Saprobity and trophic status was largely β-mesosaprobous (2) and eutraphentic (5), respectively. The Leclercq index also shows non-existent (<10%) to low (10-20%) organic pollution, degradation (IDSE=3.5-3.0) and moderate anthropogenic eutrophication (20.1-45%) in most of the streams attributed to urbanization stress (62 MLD sewage). The water quality based on indices; IBD (Indice biologique diatomèes), IPS (Indice de polluo-sensibilite) and TDI (Trophic Diatom Index) showed the moderate water quality in the streams of the Valley. Like EU Water Framework Directive 2000/60/EC (WFD) India should also have the objective to ensure ecosystem integrity through bio-assessment and not just mere pollution control.
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Halvorson, William L., Stephen Woodley, James Kay et George Francis. « Ecological Integrity and the Management of Ecosystems ». Estuaries 20, no 1 (mars 1997) : 249. http://dx.doi.org/10.2307/1352734.

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NOSS, REED F. « Can We Maintain Biological and Ecological Integrity ? » Conservation Biology 4, no 3 (septembre 1990) : 241–43. http://dx.doi.org/10.1111/j.1523-1739.1990.tb00284.x.

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Wheeler, Ben. « Ecological Integrity : Integrating Environment, Conservation and Health. » International Journal of Epidemiology 31, no 3 (juin 2002) : 704–5. http://dx.doi.org/10.1093/ije/31.3.704.

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Özesmi, Uygar, et Stacy L. Özesmi. « Ecological Integrity : Integrating Environment, Conservation, and Health ». Ecological Engineering 19, no 2 (août 2002) : 177–79. http://dx.doi.org/10.1016/s0925-8574(02)00035-6.

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Williams, Greg. « Ecological Integrity : Integrating Environment, Conservation and Health ». Agriculture, Ecosystems & ; Environment 90, no 1 (juin 2002) : 108. http://dx.doi.org/10.1016/s0167-8809(02)00023-3.

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Myers, Judith. « Ecological integrity and the management of ecosystems ». Agriculture, Ecosystems & ; Environment 49, no 3 (juillet 1994) : 309–10. http://dx.doi.org/10.1016/0167-8809(94)90060-4.

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Jørgensen, Sven Erik. « Ecological integrity and the management of ecosystems ». Ecological Economics 12, no 3 (mars 1995) : 249–50. http://dx.doi.org/10.1016/0921-8009(95)90153-1.

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Lorenz, Stefan, et Martin T. Pusch. « Estimating the recreational carrying capacity of a lowland river section ». Water Science and Technology 66, no 9 (1 novembre 2012) : 2033–39. http://dx.doi.org/10.2166/wst.2012.418.

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Recreational boating represents a major human use of inland waters in many regions. However, boating tourism may affect the ecological integrity of surface waters in multiple ways. In particular, surface waves produced by boating may disturb freshwater invertebrates, such as interrupting the filtration activity of benthic mussels. As mussels may significantly contribute to self-purification, disturbance may have crucial impacts on water quality, and thus on water tourism. In this paper we calculate the carrying capacity of a river section for sustainable boating tourism based on the preservation of water quality. This approach is complemented by spatial and social approaches for carrying capacity estimates. The ecological carrying capacity significantly decreases with lower water levels during summer. Hence, the analysis of variables that influence the river's carrying capacity allows the formation of recommendations for management measures that integrate social, touristic and ecological aspects.
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Mackey, Brendan. « The Earth Charter and Ecological Integrity—Some Policy Implications ». Worldviews : Global Religions, Culture, and Ecology 8, no 1 (2004) : 76–92. http://dx.doi.org/10.1163/1568535041337711.

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AbstractThe concept of ecological integrity is deeply embedded within the Earth Charter. Ecological integrity refers to the full functioning of a suite of natural processes. "Natural" refers to processes that exist without human input. Arguments against the scientifi c validity of ecological integrity are based on the proposition that the current state of ecological systems merely refl ects past contingencies and consequently there is no natural, healthy condition that can be prescribed scientifi cally. Hence, nature conservation and environmental management goals are a matter of individual and social values and priorities. This argument can be rejected largely on the grounds that integrity of ecosystem processes can be empirically demonstrated, and that the continued wellbeing of humanity depends on the ecological integrity of various natural processes known as Earth's life support systems. The main policy implications of ecological integrityfl ow from accepting that the future wellbeing of the human endeavour is irrevocably coupled to the ongoing integrity of the total Earth system. The caring and compassionate attitude towards wild animals also promoted by the Earth Charter provides additional moral impetus to protecting habitat in situ and consequently ecological integrity. Protecting ecological integrity will require both reorientating the human endeavour towards new patterns of production and consumption together with a commitment to making room for wild nature.
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19

Xu, Wenting. « Ecological Integrity Evaluation of Organically Evolved Cultural Landscape ». Mobile Information Systems 2022 (5 septembre 2022) : 1–11. http://dx.doi.org/10.1155/2022/9554359.

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When the traditional method is used to evaluate the cultural landscape as a whole, due to the lack of historical and cultural factors, the impact of the ecological environment on the landscape change is not considered. Therefore, it cannot objectively reflect the law of landscape change. Therefore, from the perspective of the combination of cultural landscape composition characteristics and cultural ecological characteristics, this paper puts forward the concept of cultural ecological integrity based on the existing concept of cultural heritage integrity, aiming at the organic evolution of cultural landscape in cultural landscape heritage, and expounded the dynamic sustainability and effectiveness of natural environment and social environment on the process of cultural landscape. Considering the relevant characteristics and different forms of cultural landscape and cultural ecological integrity, according to the concept of cultural ecological integrity, this paper gave the principles and standards of cultural landscape ecological integrity evaluation and put forward the evaluation method of cultural ecological integrity. At the same time, each index in the ecological integrity evaluation model was decomposed and explained. Finally, taking the cultural heritage of Long-men Grottoes as an example, the paper used the cultural and ecological integrity evaluation model proposed in this paper to evaluate the material cultural landscape, intangible cultural landscape, and local traditional dwellings of Long-men Grottoes and made a comparative analysis between the control group and the observation group. The results showed that the cultural landscape ecological integrity evaluation model proposed in this paper can not only objectively evaluate the cultural landscape but also provide a certain theoretical and practical reference for the effective classification, protection and sustainable development, and utilization of the subsequent cultural landscape.
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20

Schiesary, L. « Biodiversity and the ecological integrity of freshwater systems ». Toxicology Letters 350 (septembre 2021) : S6. http://dx.doi.org/10.1016/s0378-4274(21)00245-9.

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LaPaix, Richard, Bill Freedman et David Patriquin. « Ground vegetation as an indicator of ecological integrity ». Environmental Reviews 17, NA (décembre 2009) : 249–65. http://dx.doi.org/10.1139/a09-012.

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Indicators are being sought for monitoring the ecological integrity of forests and other kinds of ecosystems. Biological measures are commonly used as indicators because of their inherent ecological importance and ability to provide insight into environmental change. Such measures are commonly based on data from sets of permanent plots in which the abundances of plant species are monitored. However, the data may be difficult to interpret, especially if corresponding information on natural and anthropogenic stressors is lacking. In this review, we examine general principles of indicator use and discuss the types of plot-based compositional measures obtained from vegetation that may be most relevant for monitoring ecological integrity. Our focus is on the ground vegetation of forested ecosystems, but the principles discussed are relevant to other vegetation types. Individual plant species, guilds, aliens, diversity indices, Ellenberg indicator values, the floristic quality assessment index, multivariate and multimetric indicators are examined, as well as concepts of threshold changes and the need for reference states. The usefulness of any given approach tends to be highly context specific. In particular, the value of using individual species as indicators is highly dependant on factors such as the character of the floristic community of interest and the types and intensities of anthropogenic stressors. Alien species are considered to be especially valuable indicators of changes in ecological integrity due to their established relationships with anthropogenic stressors, known historical state, relevance to all floristic communities, and ability to cause undesirable changes to biodiversity and ecological processes.
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Soskolne, Colin L., et Lee E. Sieswerda. « Implementing Ethics in the Professions : Toward Ecological Integrity ». Ecosystem Health 4, no 2 (juin 1998) : 109–18. http://dx.doi.org/10.1046/j.1526-0992.1998.00078.x.

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Jiang, Mengzhen, Xiaoping Pang, Jianjun Wang et Chao Cao. « Islands ecological integrity evaluation using multi sources data ». Ocean & ; Coastal Management 158 (mai 2018) : 134–43. http://dx.doi.org/10.1016/j.ocecoaman.2018.03.033.

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Karr, James R. « Defining and assessing ecological integrity : Beyond water quality ». Environmental Toxicology and Chemistry 12, no 9 (septembre 1993) : 1521–31. http://dx.doi.org/10.1002/etc.5620120902.

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Lessmann, Janeth, Maria J. Troya, Alexander S. Flecker, W. Chris Funk, Juan M. Guayasamin, Valeria Ochoa-Herrera, N. LeRoy Poff, Esteban Suárez et Andrea C. Encalada. « Validating anthropogenic threat maps as a tool for assessing river ecological integrity in Andean–Amazon basins ». PeerJ 7 (20 novembre 2019) : e8060. http://dx.doi.org/10.7717/peerj.8060.

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Anthropogenic threat maps are commonly used as a surrogate for the ecological integrity of rivers in freshwater conservation, but a clearer understanding of their relationships is required to develop proper management plans at large scales. Here, we developed and validated empirical models that link the ecological integrity of rivers to threat maps in a large, heterogeneous and biodiverse Andean–Amazon watershed. Through fieldwork, we recorded data on aquatic invertebrate community composition, habitat quality, and physical-chemical parameters to calculate the ecological integrity of 140 streams/rivers across the basin. Simultaneously, we generated maps that describe the location, extent, and magnitude of impact of nine anthropogenic threats to freshwater systems in the basin. Through seven-fold cross-validation procedure, we found that regression models based on anthropogenic threats alone have limited power for predicting the ecological integrity of rivers. However, the prediction accuracy improved when environmental predictors (slope and elevation) were included, and more so when the predictions were carried out at a coarser scale, such as microbasins. Moreover, anthropogenic threats that amplify the incidence of other pressures (roads, human settlements and oil activities) are the most relevant predictors of ecological integrity. We concluded that threat maps can offer an overall picture of the ecological integrity pattern of the basin, becoming a useful tool for broad-scale conservation planning for freshwater ecosystems. While it is always advisable to have finer scale in situ measurements of ecological integrity, our study shows that threat maps provide fast and cost-effective results, which so often are needed for pressing management and conservation actions.
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Putri, Nurilla Elysa, Nukmal Hakim et M. Yamin. « Analisis Jejak Ekologi dan Biokapasitas untuk Pengendalian Banjir di Sumatera Selatan ». MIMBAR, Jurnal Sosial dan Pembangunan 32, no 1 (25 juin 2016) : 58. http://dx.doi.org/10.29313/mimbar.v32i1.1729.

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Planning is the beginning of development activities towards sustainable environmental urgently needed and by integrating ecological footprint into development planning in the region, especially the Spatial Plan (RTRW) that is effective and has a strong tenure. This research aims to analyze existing ecological footprint in South Sumatra, to be able to note the condition of regions ecological footprint. Data analysis is carried out through a quantitative analysis, such as calculating where Ecological Footprint (EFA) and Counting Biocapacity (BC). Results of the analysis obtained EF EF = 0.967 and 1.088 that BC = EF <BC which means undershoot, which needs space do not exceed the space available to support the population lives in the region of South Sumatra. Recommendations are given in integrating Ecologicall Footprint in South Sumatra RTRW is making patterns of spatial use directives that integrate the needs of consumption and waste disposal populations, both individually and as a community.
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Xia, Siyi. « The Construction of the Protection Mechanism of Rural Landscape in the Process of Urbanization ». Probe - Environmental Science and Technology 3, no 1 (29 avril 2021) : 17. http://dx.doi.org/10.18686/pes.v3i1.1388.

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<p>With the accelerated development of urbanization, China’s rural landscape is declining. To create a “beautiful countryside”, the first thing is to protect the existing rural landscape. There are three aspects that need to be <span style="font-family: 'Times New Roman';">considered </span>to structure the protection mechanism of rural landscape. Cultivated land is an essential part of the rural landscape. It is the basis of protecting the existing cultivated land in the countryside to establish and implement the cultivated land protection system. Rural cultural landscape is the cultural embodiment of the integration of rural society and natural environment. It should follow the principles of integrity, living and authenticity to protect the macro ecological environment and micro internal elements of the cultural landscape. Ecological conditions are closely related to the livability of the human settlement environment and cultural attribute of rural landscape. The construction of ecological civilization requires the government to take the lead and the masses to support, and then balance the benefits between ecologic and economic in the urbanization development.</p>
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Medeiros, Hugo Reis, et José Marcelo Torezan. « Evaluating the ecological integrity of Atlantic forest remnants by using rapid ecological assessment ». Environmental Monitoring and Assessment 185, no 5 (21 septembre 2012) : 4373–82. http://dx.doi.org/10.1007/s10661-012-2875-7.

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Zhang, Zhimei, Yanguo Fan et Zhijun Jiao. « Wetland ecological index and assessment of spatial-temporal changes of wetland ecological integrity ». Science of The Total Environment 862 (mars 2023) : 160741. http://dx.doi.org/10.1016/j.scitotenv.2022.160741.

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Yang, Shuhui, et Xiaoyu Duan. « Protection and enlightenment of ecological integrity of Canadian national parks ». E3S Web of Conferences 131 (2019) : 01035. http://dx.doi.org/10.1051/e3sconf/201913101035.

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Canada is one of the first countries in the world to establish a national park, and pioneered the concept of ecological integrity management of national parks. Based on this concept, the country has basically achieved the sustainable development of national parks. China has a vast territory, a large number of scenic spots and nature reserves, but its system and management methods need to be optimized. This paper takes forestry developed countries as an example, summarizes the progress of ecological integrity protection in Canadian national parks, summarizes its current ecosystem adaptive management concepts and implementation methods, Ecological Integrity (EI) monitoring construction and related evaluation index systems, ecosystem protection and restoration. The experience is intended to provide a reference for the improvement of the ecological integrity protection of national parks in China.
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Müller, Felix, Regina Hoffmann-Kroll et Hubert Wiggering. « Indicating ecosystem integrity — theoretical concepts and environmental requirements ». Ecological Modelling 130, no 1-3 (juin 2000) : 13–23. http://dx.doi.org/10.1016/s0304-3800(00)00210-6.

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Lean, Christopher Hunter. « General Unificatory Theories in Community Ecology ». Philosophical Topics 47, no 1 (2019) : 125–42. http://dx.doi.org/10.5840/philtopics20194717.

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The question of whether there are laws of nature in ecology has developed substantially in the last 20 years. Many have attempted to rehabilitate ecology’s lawlike status through establishing that ecology possesses laws that robustly appear across many different ecological systems. I argue that there is still something missing, which explains why so many have been skeptical of ecology’s lawlike status. Community ecology has struggled to establish what I call a General Unificatory Theory (GUT). The lack of a GUT causes problems for explanation as there are no guidelines for how to integrate the lower-level mathematical and causal models into a larger theory of how ecological assemblages are formed. I turn to a promising modern attempt to provide a unified higher-level explanation in ecology, presented by ecologist Mark Vellend, and advocate for philosophical engagement with its prospects for aiding ecological explanation.
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Parisod, Christian. « Polyploids integrate genomic changes and ecological shifts ». New Phytologist 193, no 2 (20 décembre 2011) : 297–300. http://dx.doi.org/10.1111/j.1469-8137.2011.04008.x.

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Wicklum, D., et Ronald W. Davies. « Ecosystem health and integrity ? » Canadian Journal of Botany 73, no 7 (1 juillet 1995) : 997–1000. http://dx.doi.org/10.1139/b95-108.

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The concepts of ecosystem health and ecosystem integrity are discussed and found to be ecologically inappropriate. The phrase ecosystem health is based on an invalid analogy with human health requiring acceptance of an optimum condition and homeostatic processes maintaining the ecosystem at a definable optimum state. Similarly, ecosystem integrity is not an objective, quantifiable property of an ecosystem. Health and integrity are not inherent properties of an ecosystem and are not supported by either empirical evidence or ecological theory. Key words: ecosystem health, ecosystem integrity, ecosystem, management, sustainability.
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Shi, Yuqiong, Ninglian Wang, Tuansheng Li, Han Wang, Huanhuan Kang et Xiaohui Shi. « Evaluation of Landscape Ecological Integrity in the Yulin Region, China ». Sustainability 10, no 11 (20 novembre 2018) : 4300. http://dx.doi.org/10.3390/su10114300.

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We developed a framework and an index to evaluate landscape ecological integrity. The framework was applied to the Yulin region (Shaanxi Province, China) to evaluate its overall ecological integrity and the effect of the Grain for Green Project on landscape ecological integrity. Landscape ecological integrity (LEI) is the ability of an ecosystem to maintain its self-organization capacity, stability, and diversity in structure and function. A landscape having high ecological integrity has three major characteristics: complex structure, high self-organization capacity, and a high level of stability. The LEI can be evaluated using five indicators: landscape fragmentation, connectance, ecological sensitivity, diversity, and vegetation productivity. The results indicate that the LEI in the Yulin region was relatively low during the period from 2000 to 2015. From 2000 to 2005, areas of very low and low LEI decreased, and areas of moderate and high LEI increased. From 2005 to 2010, areas of low and high LEI decreased, and areas of moderate LEI increased. Furthermore, from 2010 to 2015, areas of very low and low LEI increased, and areas of moderate and high LEI decreased. Overall, the LEI of the region was low, but increased between 2000 and 2010, and decreased between 2010 and 2015. On the basis of these findings, we conclude that the Grain for Green Project in the Yulin region has been successful in improving regional LEI.
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Hosbey, Justin, Hilda Lloréns et J. T. Roane. « Introduction ». Environment and Society 13, no 1 (1 septembre 2022) : 1–10. http://dx.doi.org/10.3167/ares.2022.130101.

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This collection derives from an ongoing experiment in thinking through and with the potential epistemic insurgency presented by our loose collective’s working terminology, “Black ecologies.” This term moves from the resonances between the editors’ own research in New Orleans, Puerto Rico, and Virginia, respectively. Each of us considers from our different vantages the ecological consequences of slavery and its afterlives in the enduring regime of extractivism and disposability shaping Black communities in the Diaspora. This resonance has inspired us to collaborate in various formations, including a virtual dialogue about the environment for the People’s Strike organization in July 2021, the Black Ecologies series at Black Perspectives, the virtual gathering hosted by the Black Ecologies Initiative at Arizona State University in Spring 2022, “Making Livable Worlds” (following co-editor Hilda Lloréns’ monograph title), and a zine publication, which have together added further integrity, meaning, and possibilities for thinking with this formulation outside a restrictive or proprietary vision for its potential.
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Del Gobbo, Giovanna, Francesco De Maria et Marta Pampaloni. « Sustainable development in higher education : an integrated teaching and research experience ». Form@re - Open Journal per la formazione in rete 21, no 2 (31 juillet 2021) : 46–63. http://dx.doi.org/10.36253/form-11418.

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The contribution presents a teaching experience in a master’s degree program of ​​the University of Florence in pedagogical area. Through an integrated research-informed teaching (RIT) approach and the use of active methodologies, the course focuses on the topics of Agenda 2030 and sustainability, dealing with educational dimension underlying development’s actions. The importance of student-centred and learning outcomes-oriented pedagogical and didactic approaches are highlighted. These are functional to the development of competences linked to the theme of sustainable development, but also oriented towards the training of education professionals who are considered central figures in the accompaniment and management of ecological and sustainable transition processes. The contribution offers the systematization of this long-term experience in university teaching. Lo sviluppo sostenibile nell’alta formazione: un’esperienza integrata di didattica e ricerca Il contributo presenta un’esperienza di insegnamento all’interno di un corso di laurea magistrale di area pedagogica dell’Università di Firenze. Attraverso un approccio integrato di research-informed teaching (RIT) e l’utilizzo di metodologie attive, il corso è centrato sui temi dell’Agenda 2030 e della sostenibilità, esplicitando la dimensione educativa sottesa alle azioni di sviluppo. Si evidenzia l’importanza di approcci pedagogici e didattici student centred e learning outcomes oriented funzionali allo sviluppo di competenze legate al tema dello sviluppo sostenibile e volti alla formazione di professionisti dell’educazione e della formazione ritenuti figure centrali nell’accompagnamento e nella gestione di processi di transizione ecologica e sostenibile. Il contributo offre la sistematizzazione di questa esperienza pluriennale di didattica universitaria.
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Tierney, Geraldine L., Don Faber-Langendoen, Brian R. Mitchell, W. Gregory Shriver et James P. Gibbs. « Monitoring and evaluating the ecological integrity of forest ecosystems ». Frontiers in Ecology and the Environment 7, no 6 (août 2009) : 308–16. http://dx.doi.org/10.1890/070176.

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Camhi, Merry. « Industrial Fisheries Threaten Ecological Integrity of the Galapagos Islands ». Conservation Biology 9, no 4 (août 1995) : 715–19. http://dx.doi.org/10.1046/j.1523-1739.1995.09040715.x.

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JUNGWIRTH, M., S. MUHAR et S. SCHMUTZ. « Re-establishing and assessing ecological integrity in riverine landscapes ». Freshwater Biology 47, no 4 (avril 2002) : 867–87. http://dx.doi.org/10.1046/j.1365-2427.2002.00914.x.

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Kim, Rakhyun E., et Klaus Bosselmann. « Operationalizing Sustainable Development : Ecological Integrity as aGrundnormof International Law ». Review of European, Comparative & ; International Environmental Law 24, no 2 (5 juin 2015) : 194–208. http://dx.doi.org/10.1111/reel.12109.

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Rapport, David J. « Ecosystem Health, Ecological Integrity, and Sustainable Development : Toward Consilience ». Ecosystem Health 4, no 3 (septembre 1998) : 145–46. http://dx.doi.org/10.1046/j.1526-0992.1998.00085.x.

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Quigley, Thomas M., Richard W. Haynes et Wendel J. Hann. « Estimating ecological integrity in the interior Columbia River basin ». Forest Ecology and Management 153, no 1-3 (octobre 2001) : 161–78. http://dx.doi.org/10.1016/s0378-1127(01)00459-5.

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Santmire, H. Paul. « Book Review : Loving Nature : Ecological Integrity and Christian Responsibility ». Interpretation : A Journal of Bible and Theology 47, no 3 (juillet 1993) : 332–34. http://dx.doi.org/10.1177/002096430004700334.

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Calow, Peter. « Book Review : Interconnections Between Human Health and Ecological Integrity ». Environmental Science & ; Technology 37, no 3 (février 2003) : 71A. http://dx.doi.org/10.1021/es032347i.

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Wurtzebach, Zachary, et Courtney Schultz. « Measuring Ecological Integrity : History, Practical Applications, and Research Opportunities ». BioScience 66, no 6 (13 avril 2016) : 446–57. http://dx.doi.org/10.1093/biosci/biw037.

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Kupfer, John A., et Peng Gao. « Spatial Patterns of Ecological Integrity in South Carolina Watersheds ». Southeastern Geographer 51, no 3 (2011) : 394–410. http://dx.doi.org/10.1353/sgo.2011.0029.

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Chernov, Yu I. « Ecological integrity of supraspecific taxa and the arctic biota ». Entomological Review 88, no 9 (décembre 2008) : 1019–31. http://dx.doi.org/10.1134/s0013873808090017.

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Bedoya, David, Vladimir Novotny et Elias S. Manolakos. « Instream and offstream environmental conditions and stream biotic integrity ». Ecological Modelling 220, no 19 (octobre 2009) : 2393–406. http://dx.doi.org/10.1016/j.ecolmodel.2009.06.017.

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Shaker, Richard R., et Timothy J. Ehlinger. « Exploring Non-Linear Relationships between Landscape and Aquatic Ecological Condition in Southern Wisconsin ». International Journal of Applied Geospatial Research 5, no 4 (octobre 2014) : 1–20. http://dx.doi.org/10.4018/ijagr.2014100101.

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Recent studies have implied the importance of incorporating configuration metrics into landscape-aquatic ecological integrity research; however few have addressed the needs of spatial data while exploring non-linear relationships. This study investigates spatial dependence of a measure of aquatic ecological condition at two basin scales, and the spatial and non-linear role of landscape in explaining that measure across 92 watersheds in Southern Wisconsin. It hypothesizes that: (1) indicators of ecological condition have different spatial needs at subwatershed and watershed scales; (2) land cover composition, urban configuration, and landscape diversity can explain aquatic ecological integrity differently; and (3) global non-linear analysis improve local spatial statistical techniques for explaining and interpreting landscape impacts on aquatic ecological integrity. Results revealed spatial autocorrelation in the measure of aquatic ecological condition at the HUC-12 subwatershed scale, and artificial neural networks (ANN) were an improvement over geographically weighted regression (GWR) for deciphering complex landscape-aquatic condition relationships.
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