No retraction, correction or concern found when last checked on Oct 23, 2026.
Instruments for Assessing Risk of Bias and Other Methodological Criteria of Published Animal Studies: A Systematic Review
David Krauth, Tracey J. Woodruff, Lisa Bero
Environmental Health Perspectives · 2013 · Systematic review · Public domain
Abstract
Background: Results from animal toxicology studies are critical to evaluating the potential harm from exposure to environmental chemicals or the safety of drugs prior to human testing. However, there is significant debate about how to evaluate the methodology and potential biases of the animal studies. There is no agreed-upon approach, and a systematic evaluation of current best practices is lacking. Objective: We performed a systematic review to identify and evaluate instruments for assessing the risk of bias and/or other methodological criteria of animal studies. Method: We searched Medline (January 1966–November 2011) to identify all relevant articles. We extracted data on risk of bias criteria (e.g., randomization, blinding, allocation concealment) and other study design features included in each assessment instrument. Discussion: Thirty distinct instruments were identified, with the total number of assessed risk of bias, methodological, and/or reporting criteria ranging from 2 to 25. The most common criteria assessed were randomization (25/30, 83%), investigator blinding (23/30, 77%), and sample size calculation (18/30, 60%). In general, authors failed to empirically justify why these or other criteria were included. Nearly all (28/30, 93%) of the instruments have not been rigorously tested for validity or reliability. Conclusion: Our review highlights a number of risk of bias assessment criteria that have been empirically tested for animal research, including randomization, concealment of allocation, blinding, and accounting for all animals. In addition, there is a need for empirically testing additional methodological criteria and assessing the validity and reliability of a standard risk of bias assessment instrument. Citation: Krauth D, Woodruff TJ, Bero L. 2013. Instruments for assessing risk of bias and other methodological criteria of published animal studies: a systematic review. Environ Health Perspect 121:985–992 (2013); http://dx.doi.org/10.1289/ehp.1206389
Full text
From PubMed Central, U.S. National Library of Medicine, as current on Oct 23, 2026. Paragraph numbers are ours, so an answer can point at one.
Introduction
Results from animal toxicology studies are a critical—and often the only—input to evaluating potential harm from exposure to environmental chemicals or the safety of drugs before they proceed to human testing. However, there is significant debate about how to use animal studies in risk assessments and other regulatory decisions. An important part of this debate is how to evaluate the methodology and potential biases of the animal studies in order to establish how confident one can be in the data.
For the evaluation of human clinical research, there is a distinction between assessing risk of bias and methodological quality. Risks of bias are methodological criteria of a study that can introduce a systematic error in the magnitude or direction of the results. In controlled human clinical trials testing the efficacy of drugs, studies with a high risk of bias—such as those lacking randomization, allocation concealment, or blinding of participants, personnel, and outcome assessors—produce larger treatment effect sizes, thus falsely inflating the efficacy of the drugs compared with studies that have these design features (Schulz et al. 1995;, ). Biased human studies assessing the harms of drugs are less likely to report statistically significant adverse effects. An assessment of a study’s methodology includes evaluation of additional study criteria related to how a study is conducted (e.g., in compliance with human subjects guidelines) or reported (e.g., study population described). Finally, risk of bias is not the same as imprecision. Whereas bias refers to systematic error, imprecision refers to random error. Although smaller studies are less precise, they may not be more biased.
Although there is a well-developed and empirically based literature on how to evaluate the risk of bias of randomized controlled clinical trials, less is known about how to do this for animal studies. Some risks of bias in animal studies have been identified empirically. For example, analyses of animal studies examining interventions for stroke, multiple sclerosis, and emergency medicine have shown that lack of randomization, blinding, specification of inclusion/exclusion criteria, statistical power, and use of comorbid animals are associated with inflated effect estimates of pharmaceutical interventions. However, these studies used a variety of instruments to evaluate the methodology of animal studies and often mixed assessment of risks of bias, reporting, and other study criteria.
Several guidelines and instruments for evaluating the risks of bias and other methodological criteria of animal research have been published, but there has been no attempt to compare the criteria that they include; to determine whether risk of bias, reporting, or other criteria are assessed; or to determine whether the criteria are based on empirical evidence of bias. The purpose of this review was 2-fold: a) to systematically identify and summarize existing instruments for assessing risks of bias and other methodological criteria of animal studies, and b) to highlight the criteria that have been empirically tested for an association with bias in either animal or clinical models.
Methods
Inclusion/exclusion criteria. Articles that met the following inclusion criteria were included: a) The article was a published report focusing on the development of an instrument for assessing the methodology of animal studies, and b) the article was in English. Where multiple analyses using a single instrument were published separately, the earliest publication was used. Modifications or updates of previously published instruments were considered new instruments and included. We did not include applications of previously reported instruments that were used, for example, to assess a certain area of animal research.
Search strategy. We searched Medline for articles published from January 1966 through November 2011 using a search term combination developed with input from expert librarians. Bibliographies from relevant articles were also screened to find any remaining articles that were not captured from the Medline search. Our search strategy contained the following MeSH terms, text words, and word variants:
{(animal experimentation[mh]) AND (standards[sh] OR research design[mh] OR bias[tw] OR biases[tw] OR checklist*[tw] OR translational research/ethics)} OR {(animals, laboratory[majr] OR disease models, animal[mh] OR drug evaluation, preclinical[mh] OR chemical evaluation OR chemical toxicity OR chemical safety) AND (research[majr:noexp] OR translational research[majr] OR research design[majr] OR “quality criteria”) AND (guideline* OR bias[tw] OR biases[tiab] OR reporting[tw])} OR {(animal*[ti] OR preclinical[ti] OR pre-clinical[ti] OR toxicology OR toxicological OR ecotoxicology OR environmental toxicology) AND (methodological quality OR research reporting OR study quality OR “risk of bias” OR “weight of evidence”)} OR {(CAMARADES[tiab] OR “gold standard publication checklist” OR exclusion inclusion criteria animals bias) OR (peer review, research/standards AND Animals[Mesh:noexp])} OR {(models, biological[mh] OR drug evaluation, preclinical[mh] OR toxicology[mh] OR disease models, animal[majr]) AND (research design[mh] OR reproducibility of results[mh] OR “experimental design”) AND (quality control[mh] OR guidelines as topic[mh] OR bias[tw] OR “critical appraisal”) AND (Animals[Mesh:noexp])} AND eng[la].
Article selection. Studies were screened in two stages. Initially, we reviewed abstracts and article titles, and only those articles meeting our inclusion criteria were further scrutinized by reading the full text. Any articles that did not clearly meet the criteria after review of the full text were discussed by two authors, who made the decision about inclusion. Exact article duplicates were removed using Endnote X2 software (Thomson Reuters, Carlsbad, CA).
Data extraction. We extracted data on each criterion included in each instrument, as well as information on how the instrument was developed.
Instrument development and characteristics. We recorded the method used to develop each instrument (i.e., whether the criteria in the instrument were selected based on consensus, previous animal instruments, and/or clinical instruments). We also recorded whether or not the criteria in the instrument were empirically tested to determine if they were associated with biased effect estimates. Empirical testing was rated as completed if at least one of the individual criterion was empirically tested.
Numerical methodological “quality” scores have been shown to be invalid for assessing risk of bias in clinical research. The current standard in evaluating clinical research is to report each component of the assessment instrument separately and not calculate an overall numeric score. Although the use of quality scores is now considered inappropriate, it is still a common practice. Therefore, we also assessed whether and how each instrument calculated a “quality” score.
We also noted whether the instrument had been tested for reliability and validity. Reliability in assessing risk of bias refers to the extent to which results are consistent between different coders or in trials or measurements that are repeated. Validity refers to whether the instrument measures what it was intended to measure, that is, methodological features that could affect research outcomes.
Study design criteria to assess risk of bias and other methodological criteria. Based on published risk of bias assessment instruments for clinical research, we developed an a priori list of criteria and included additional criteria if they occurred in the review of the animal instruments.
We collected risk of bias, methodological, and reporting criteria because these three types of assessment criteria were often mixed in the individual instruments. The final list of these criteria is as follows:
Treatment allocation/randomization. Describes whether or not treatment was randomly allocated to animal subjects so that each subject has an equal likelihood of receiving the intervention.
Concealment of allocation. Describes whether or not procedures were used to protect against selection bias by ensuring that the treatment to be allocated is not known by the investigator before the subject enters the study.
Blinding. Relates to whether or not the investigator involved with performing the experiment, collecting data, and/or assessing the outcome of the experiment was unaware of which subjects received the treatment and which did not.
Inclusion/exclusion criteria. Describes the process used for including or excluding subjects.
Sample size calculation. Describes how the total number of animals used in the study was determined.
Compliance with animal welfare requirements. Describes whether or not the research investigators complied with animal welfare regulations.
Financial conflict of interest. Describes if the investigator(s) disclosed whether or not he/she has a financial conflict of interest.
Statistical model explained. Describes whether the statistical methods used and the unit of analysis are stated and whether the statistical methods are appropriate to address the research question.
Use of animals with comorbidity. Describes whether or not the animals used in the study have one or more preexisting conditions that place them at greater risk of developing the health outcome of interest or responding differently to the intervention relative to animals without that condition.
Test animal descriptions. Describes the test animal characteristics including animal species, strain, substrain, genetic background, age, supplier, sex, and weight. At least one of these characteristics must be present for this criterion to be met.
Dose–response model. Describes whether or not an appropriate dose–response model was used given the research question and disease being modeled.
All animals accounted for. Describes whether or not the investigator accounts for attrition bias by providing details about when animals were removed from the study and for what reason they were removed.
Optimal time window investigated. Describes whether or not the investigator allowed sufficient time to pass before assessing the outcome. The optimal time window used in animal research should reflect the time needed to see the outcome and depends on the hypothesis being tested. The optimal time window investigated should not be confused with the “therapeutic time window of treatment,” which is defined as the time interval after exposure or onset of disease during which an intervention can still be effectively administered.
We extracted data on the study design criteria assessed by each instrument. We recorded the number of criteria assessed for each instrument, excluding criteria related only to journal reporting requirements (i.e., headers in an abstract).
Analysis. Here we report the frequency of each criterion assessed, as well as the frequency of any additional criteria that were included in the instruments.
Results
As shown in Figure 1, we identified 3,731 potentially relevant articles. After screening the article titles and abstracts, we identified 88 citations for full text evaluation. After reviewing full text, 60 papers were excluded for at least one of three reasons: a) They did not meet inclusion criteria; b) the studies reviewed a preexisting instrument; and c) the article reported application of an instrument. After screening bibliographies, two additional instruments were found. Overall, 30 instruments were identified and included in the final analysis.
Table 1 lists the criteria of each instrument. Of the 30 instruments, 13 were derived by modifying or updating previously developed animal research methodology assessment instruments or citing animal studies supporting the inclusion of specific criteria; 3 were derived from previously developed clinically based risk of bias assessment instruments or citing clinical studies supporting the inclusion of specific criteria; 5 were developed using evidence from clinical research and either through consensus or citing past instrument publications; 3 were developed through consensus and citing past publications; and 6 had no description of how they were developed.
Six instruments contained at least one criterion that showed an association of the criterion with inflated drug efficacy in animal models.
Seven instruments calculated a score for assessing methodological “quality.” Descriptions of how these scores were calculated are provided in Table 1. Sixteen of the instruments were designed for no specific disease model; the most commonly modeled disease was stroke (9 of 30 instruments).
Only 1 instrument was tested for validity, and 1 instrument was tested for reliability. Overall, 18 instruments were designed specifically to evaluate preclinical drug studies, 8 instruments documented general animal research guidelines, and 4 instruments were designed to assess environmental toxicology research.
The total number of risk of bias, methodological, and/or reporting criteria assessed by each instrument ranged from 2 to 25. Table 2 shows the study design criteria used to assess risk of bias for each of the 30 instruments. Although these criteria were included in at least some of the instruments, they were not all supported by empirical evidence of bias. Blinding and randomization were the two most common criteria found in existing instruments; 25 instruments included randomization and 23 instruments included blinding. The need to provide a sample size calculation was listed in 18 instruments. None of the instruments contained all 13 criteria from our initial list; 2 instruments contained 9 criteria, and 4 instruments contained only 1 or 2 of the criteria.
Additional criteria assessed by each instrument are listed in Supplemental Material, Table S1. Some of these criteria related to reporting requirements for the abstract, introduction, methods, results, and conclusions, rather than risk of bias criteria. These reporting criteria were not included in the count for the number of risk of bias criteria assessed by an instrument. For example, stated that the ARRIVE Guidelines is a 20-criteria instrument. However, we consider the ARRIVE Guidelines as a 13-criteria instrument because 7 of the original criteria pertain to reporting requirements. Fourteen instruments contained criteria to describe animal housing, husbandry, or physiological conditions. Inclusion of these criteria is empirically supported by studies showing that changes in housing conditions affect physiological and behavioral parameters in rodents. Among instruments that did not specify the need to use randomization, 4 of 5 instruments stated that a control group should be used.
Discussion
In this systematic review we identified 30 instruments for assessing risk of bias and other methodological criteria of animal research. Identifying bias, the systematic error or deviation from the truth in actual results or inferences, in animal research is important because animal studies are often the major or only evidence that forms the basis for regulatory or further research decisions. Our review highlights the variability in the development and content of instruments that are currently used to assess bias in animal research.
Most of the instruments were not tested for reliability or validity. One notable exception is the CAMARADES (Collaborative Approach to Meta-Analysis and Review of Animal Data from Experimental Studies) instrument developed by; these authors combined criteria from four previous instruments and showed that the instrument appears to have validity. Similarly, tested the reliability of a modified version of the Australasian ecotoxicity database (AED) instrument and found an improvement in reliability compared with the original AED instrument. Furthermore, most of the instruments were not developed on the basis of empirical evidence showing an association between specific study design criteria and bias in research outcomes. Only six instruments included criteria that were supported by data showing an association between a particular methodological criterion and effect size in animal studies. Most of the instruments contain criteria based on expert judgment, and others extrapolate from evidence of risk of bias in human studies. In addition, seven instruments calculated a “quality score”; however, these scores are not considered a valid measure of risk of bias, and this practice should be discontinued.
Types of bias that are known to influence the results of research include selection, performance, detection, and exclusion. These biases have been demonstrated in animal studies, and methodological criteria that can protect against the biases have been empirically tested.
Selection bias, which introduces systematic differences between baseline characteristics in treatment and control groups, can be minimized by randomization and concealment of allocation. Lack of randomization or concealment of allocation in animal studies biases research outcomes by altering effect sizes. Performance bias is the systematic difference between treatment and control groups with regard to care or exposure other than the intervention. Detection bias refers to systematic differences between treatment and control groups with regard to how outcomes are assessed. Blinding of investigators can protect against performance bias, and there is substantial evidence that lack of blinding in a variety of types of animal studies is associated with exaggerated effect sizes. Blinding of outcome assessors is a primary way of reducing detection bias. There are many ways to achieve adequate blinding in animal studies, such as having coded data (blinding to treatment assignment) analyzed by a statistician who is independent of the rest of the research team. Exclusion bias refers to the systematic difference between treatment and control groups in the number of animals that were included in and completed the study. Accounting for all animals used in the study and using intention-to-treat analysis can reduce exclusion bias.
Some criteria included in the animal research assessment instruments are not associated with bias. For example, a statement of compliance with animal welfare requirements is a reporting issue. Sample size calculations are often included as a criterion in animal research assessment instruments, but bias is not the same as imprecision. Whereas bias refers to systematic error, imprecision refers to random error, meaning that multiple replications of the same study will produce different effect estimates because of sampling variation. Although larger and more precise studies may give a more accurate estimate of an effect, they are not necessarily less biased. Furthermore, sample size calculations can be greatly affected by the underlying assumptions made for the calculation. Although a sample size calculation is not a risk of bias criterion, it is an important characteristic to consider in evaluating an overall body of evidence.
Some of the criteria listed in the instruments are unique to animal studies. For example, in preclinical drug research, testing animals with comorbidities is necessary to identify whether or not candidate drugs retain efficacy in light of additional health complications and to more closely resemble the health status of humans. Empirical evidence supports the use of this criterion because studies that included healthy animals instead of animals with comorbidities overestimated the effect sizes of experimental stroke interventions by > 10%. For environmental chemicals, use of comorbid animals could result in the opposite influence on effect size (i.e., to decrease it), and considering this as a criterion is consistent with recommendations to evaluate the influence of biological factors that may influence risk. Timing of exposure also influences study outcome, and some effects may be observed only for exposures that occur during certain developmental periods. Sex, the nutritional status of experimental animals, and animal housing and husbandry conditions could also affect the response to an intervention or environmental chemical exposure, but these criteria should be studied to determine if they introduce a systematic bias in results. These unique criteria have not been sufficiently included in the study instruments; even if these criteria do not produce systematic bias, they should be clearly described and reported in animal studies to aid interpretation of the findings (Marshall et al. 2005).
Although some risk of bias criteria have been investigated primarily in human studies, they warrant consideration for animal studies. Reviews of clinical studies have shown that study funding sources and financial ties of investigators (including university- or industry-affiliated investigators) are associated with favorable research outcomes for the sponsors. In that study, favorable research outcomes were defined as either increased effect sizes for drug efficacy studies, or decreased effect sizes for studies of drug harm. Selective reporting of outcomes and failure to publish entire studies is considered an important source of bias in clinical studies; however, little is known about the extent of this bias in animal research.
Further research should consider potential interactions between criteria for assessing risk of bias. Existing instruments have tested the association of study design criteria on effect size using univariate models. Multiple regression models should be used to ascertain the relationship between a study design criterion and effect size when taking into account other criteria in the model. Covariance between methodological criteria should also be examined. For example, randomized studies may be less likely to omit blinding than nonrandomized studies. Knowing the relative importance of these criteria will provide additional support for inclusion of specific criteria in risk of bias assessment instruments.
Most of the instruments identified for our study exclude some criteria that appear to be important for assessing bias in animal studies (e.g., allocation concealment). It is important to recognize that some authors purposely exclude certain criteria from their instruments to reduce complexity and unnecessary detail. The most complex instrument had 25 criteria. The detailed level of reporting needed to apply the gold standard publication checklist (GSPC), which has 17 criteria, was one of the main criticisms against it.
Because many journals now allow online publication of supplemental data, risk of bias assessment should be less limited by a lack of space for reporting detailed methods. Reporting of clinical research has improved because risk of bias assessments for systematic reviews and other purposes have become more prevalent and standards for reporting have been implemented by journals. Recent calls for reporting criteria for animal studies recognize the need for improved reporting of animal research. As happened for clinical research, reporting of animal research is likely to improve if risk of bias assessments become more common.
Many of the instruments identified in our review were derived to evaluate preclinical animal drug research, which could limit their potential application in environmental health research. Although selection, detection, and performance biases are relevant for all animal research, some of the preclinical instruments contain criteria specific for assessing the quality of stroke research, such as the “avoidance of anesthetics with marked intrinsic neuroprotective properties”. On the other hand, investigation of an optimal time window for outcome assessment, the timing of the exposure, and measurement of outcomes that are sensitive to the exposure at the appropriate time are particularly important for assessing animal studies of environmental exposures.
Study limitations. A limitation of our study is that we may not have identified all published assessment instruments for animal research. Our inclusion criteria allowed only articles published in English; therefore, we may have missed some instruments published in other languages. Furthermore, because we limited our search to articles indexed in Medline, articles indexed exclusively in Embase or some other database would have been missed. However, both our consultation with a librarian and the large pool of studies identified through the electronic search suggest that it was comprehensive.
Conclusions
In this review we identified a wide variety of instruments developed to evaluate animal studies. The individual criteria included in animal risk of bias assessment instruments should be empirically tested to determine their influence on research outcomes. Furthermore, these instruments need to be tested for validity and reliability. Finally, existing instruments (many of which were developed using stroke models) need to be tested on other animal models to ensure their relevance and generalizability to other systems.
References 72
- 1.
Adami HO, Berry SC, Breckenridge CB, Smith LL, Swenberg JA, Trichopoulos D, et al. Toxicology and epidemiology: improving the science with a framework for combining toxicological and epidemiological evidence to establish causal inference. Toxicol Sci. 2011;122(2):223-234.
Not in our library10.1093/toxsci/kfr113
- 2.
Agerstrand M, Kuster A, Bachmann J, Breitholtz M, Ebert I, Rechenberg B, et al. Reporting and evaluation criteria as means towards a transparent use of ecotoxicity data for environmental risk assessment of pharmaceuticals. Environ Pollut. 2011;159(10):2487-2492.
Not in our library10.1016/j.envpol.2011.06.023
- 3.
Statistical Guidelines for Contributors to Medical Journals. 2nd ed. 2000.
Not in our library10.1136/bmj.286.6376.1489
- 4.
Altman DG, Schulz KF, Moher D, Egger M, Davidoff F, Elbourne D, et al. The revised CONSORT statement for reporting randomized trials: explanation and elaboration. Ann Intern Med. 2001;134(8):663-694.
Not in our library10.7326/0003-4819-134-8-200104170-00012
- 5.
- 6.
Bebarta V, Luyten D, Heard K. Emergency medicine animal research: does use of randomization and blinding affect the results? Acad Emerg Med. 2003;10(6):684-687.
Not in our library10.1111/j.1553-2712.2003.tb00056.x
- 7.
Benatar M. Lost in translation: treatment trials in the SOD1 mouse and in human ALS. Neurobiol Dis. 2007;26(1):1-13.
Not in our library10.1016/j.nbd.2006.12.015
- 8.
Candelario-Jalil E Mhadu NH González-Falcón A García-Cabrera M Muñoz E León OS 2005 Effects of the cyclooxygenase-2 inhibitor nimesulide on cerebral infarction and neurological deficits induced by permanent middle cerebral artery occlusion in the rat.J Neuroinflammation23;[Online 18 January 2005]
Not in our library10.1186/1742-2094-2-3
- 9.
1979.
Not in our library
- 10.
Cho MK, Bero LA. Instruments for assessing the quality of drug studies published in the medical literature. JAMA. 1994;272(2):101-104.
Not in our library
- 11.
Conrad JW Jr Becker RA 2010 Enhancing credibility of chemical safety studies: emerging consensus on key assessment criteria.Environ Health Perspect119757764;[Online 15 December 2010]
Not in our library10.1289/ehp.1002737
- 12.
Crossley NA, Sena E, Goehler J, Horn J, van der Worp B, Bath PM, et al. Empirical evidence of bias in the design of experimental stroke studies: a metaepidemiologic approach. Stroke. 2008;39(3):929-934.
Not in our library10.1161/strokeaha.107.498725
- 13.
de Aguilar-Nascimento JE. Fundamental steps in experimental design for animal studies. Acta Cir Bras. 2005;20(1):2-8.
Not in our library10.1590/s0102-86502005000100002
- 14.
Dirnagl U. Bench to bedside: the quest for quality in experimental stroke research. J Cereb Blood Flow Metab. 2006;26:1465-1478.
Not in our library10.1038/sj.jcbfm.9600298
- 15.
Duke JL, Zammit TG, Lawson DM. The effects of routine cage-changing on cardiovascular and behavioral parameters in male Sprague-Dawley rats. Contemp Top Lab Anim Sci. 2001;40(1):17-20.
Not in our library
- 16.
Durda JL, Preziosi DV. Data quality evaluation of toxicological studies used to derive ecotoxicological benchmarks. Hum Ecol Risk Assess. 2000;6(5):747-765.
Not in our library
- 17.
Framework for the Integration of Human and Animal Data in Chemical Risk Assessment. Technical Report No. 104. Brussels:European Centre for Ecotoxicology and Toxicology of Chemicals. 2009.
Not in our library
- 18.
Festing MF. Guidelines for the design and statistical analysis of experiments in papers submitted to ATLA. Altern Lab Anim. 2001;29(4):427-446.
Not in our library10.1177/026119290102900409
- 19.
Festing MF. Principles: the need for better experimental design. Trends Pharmacol Sci. 2003;24(7):341-345.
Not in our library10.1016/s0165-6147(03)00159-7
- 20.
Festing MF, Altman DG. Guidelines for the design and statistical analysis of experiments using laboratory animals. ILAR J. 2002;43(4):244-258.
Not in our library10.1093/ilar.43.4.244
- 21.
Guidelines for reviewing manuscripts on studies involving live animals. Synopsis of the workship. 1997.
Not in our library
- 22.
Fisher M, Feuerstein G, Howells DW, Hurn PD, Kent TA, Savitz SI, et al. Update of the Stroke Therapy Academic Industry Roundtable preclinical recommendations. Stroke. 2009;40(6):2244-2250.
Not in our library10.1161/strokeaha.108.541128
- 23.
Gerdin AK, Igosheva N, Roberson LA, Ismail O, Karp N, Sanderson M, et al. Experimental and husbandry procedures as potential modifiers of the results of phenotyping tests. Physiol Behav. 2012;106(5):602-611.
Not in our library10.1016/j.physbeh.2012.03.026
- 24.
Golafshani N. Understanding reliability and validity in qualitative research. Qualitative Rep. 2003;8(4):597-607.
Not in our library
- 25.
Hart B Lundh A Bero L 2012 Effect of reporting bias on meta-analyses of drug trials: reanalysis of meta-analyses.BMJ344d7202; http//dx..org/[Online 3 January 2012]
Not in our library10.1136/bmj.d7202
- 26.
Cochrane Handbook for Systematic Reviews of Interventions. 2008.
Not in our library
- 27.
Hobbs DA, Warne MSJ, Markich SJ. Evaluation of criteria used to assess the quality of aquatic toxicity data. Integr Environ Assess Manag. 2005;1(3):174-180.
Not in our library10.1897/2004-003r.1
- 28.
Hooijmans CR, Leenaars M, Ritskes-Hoitinga M. A gold standard publication checklist to improve the quality of animal studies, to fully integrate the Three Rs, and to make systematic reviews more feasible. Altern Lab Anim. 2010;38(2):167-182.
Not in our library10.1177/026119291003800208
- 29.
Horn J, de Haan RJ, Vermeulen M, Luiten PG, Limburg M. Nimodipine in animal model experiments of focal cerebral ischemia: a systematic review. Stroke. 2001;32(10):2433-2438.
Not in our library10.1161/hs1001.096009
- 30.
Hsu CY. Criteria for valid preclinical trials using animal stroke models. Stroke. 1993;24(5):633-636.
Not in our library10.1161/01.str.24.5.633
- 31.
Jadad AR, Moore RA, Carroll D, Jenkinson C, Reynolds DJ, Gavaghan DJ, et al. Assessing the quality of reports of randomized clinical trials: is blinding necessary? Control Clin Trials. 1996;17(1):1-12.
Not in our library10.1016/0197-2456(95)00134-4
- 32.
Johnson PD, Besselsen DG. Practical aspects of experimental design in animal research. ILAR J. 2002;43(4):202-206.
Not in our library10.1093/ilar.43.4.202
- 33.
Jonas S, Ayigari V, Viera D, Waterman P. Neuroprotection against cerebral ischemia. A review of animal studies and correlation with human trial results. Ann NY Acad Sci. 1999;890:2-3.
Not in our library10.1111/j.1749-6632.1999.tb07975.x
- 34.
Jüni P, Witschi A, Bloch R, Egger M. The hazards of scoring the quality of clinical trials for meta-analysis. JAMA. 1999;282(11):1054-1060.
Not in our library10.1001/jama.282.11.1054
- 35.
- 36.
Klimisch HJ, Andreae M, Tillmann U. A systematic approach for evaluating the quality of experimental toxicological and ecotoxicological data. Regul Toxicol Pharmacol. 1997;25(1):1-5.
Not in our library10.1006/rtph.1996.1076
- 37.
Lamontagne F, Briel M, Duffett M, Fox-Robichaud A, Cook DJ, Guyatt G, et al. Systematic review of reviews including animal studies addressing therapeutic interventions for sepsis. Crit Care Med. 2010;38(12):2401-2408.
Not in our library10.1097/ccm.0b013e3181fa0468
- 38.
Landis SC, Amara SG, Asadullah K, Austin CP, Blumenstein R, Bradley EW, et al. A call for transparent reporting to optimize the predictive value of preclinical research. Nature. 2012;490(7419):187-191.
Not in our library10.1038/nature11556
- 39.
Lucas C, Criens-Poublon LJ, Cockrell CT, de Haan RJ. Wound healing in cell studies and animal model experiments by low level laser therapy; were clinical studies justified? A systematic review. Lasers Med Sci. 2002;17(2):110-134.
Not in our library10.1007/s101030200018
- 40.
Lundh A Lexchin J Sismondo S Busuioc O Bero L 2011 Industry sponsorship and research outcome.Cochrane Database Syst Rev12MR000033;[Online 12 December 2012]
Not in our library10.1002/14651858.mr000033.pub2
Cited by papers we hold 9
- Effects of mesenchymal stem cells in renovascular disease of preclinical and clinical studies: a systematic review and meta-analysis · 2022Not checked
- Facilitating healthcare decisions by assessing the certainty in the evidence from preclinical animal studies · 2018No notice
- Application of the Navigation Guide systematic review methodology to the evidence for developmental and reproductive toxicity of triclosan · 2016Not checked
- Pain and Laboratory Animals: Publication Practices for Better Data Reproducibility and Better Animal Welfare · 2016No notice
- The Navigation Guide—Evidence-Based Medicine Meets Environmental Health: Systematic Review of Human Evidence for PFOA Effects on Fetal Growth · 2014No notice
- The Navigation Guide Systematic Review Methodology: A Rigorous and Transparent Method for Translating Environmental Health Science into Better Health Outcomes · 2014No notice
- SYRCLE’s risk of bias tool for animal studies · 2014No notice
- The Navigation Guide—Evidence-Based Medicine Meets Environmental Health: Systematic Review of Nonhuman Evidence for PFOA Effects on Fetal Growth · 2014No notice
- The Navigation Guide—Evidence-Based Medicine Meets Environmental Health: Integration of Animal and Human Evidence for PFOA Effects on Fetal Growth · 2014No notice
Reads
Read by people on this page
None yet.
Checked or read by AI through naulon
None yet.
A person counts once a day per paper. We keep no cookie and no address: a reader is a hash that changes every day. Any month under five reads shows no number.
Are you an author?
Is this your paper?
Claim it to add your note and be paid when agents cite it. Free.