Skip to main content

Table 1 Mesoamerican studies assessing the role of pesticides in CKD

From: Pesticide exposures and chronic kidney disease of unknown etiology: an epidemiologic review

Reference & country

Study design

Study population

Pesticide exposure assessment

Case definition/outcome(s)

Main findings

Pesticide association

-------------

Validity and explanation valuea

Rugama et al., 2001 [85]

Nicaragua

Retrospective hospital-based case-control

CKD hospitalizations during 2000: 165 cases, 334 non-CKD random hospital controls

Pesticide use yes/no, extracted from clinical records

CKD diagnosis at admission

OR pesticide exposure = 5.5 [2.8 – 10.7]

Positive association with pesticide exposure

-------------

Prevalent cases; high risk of bias from exposure misclassification; high risk of confounding

Explanation value: low

Gracía-Trabanino et al., 2005 [86]

El Salvador

Cross-sectional survey

Volunteer sample of 353 adult M, 292 coastal and 62 at 500 m above sea level (masl)

Questionnaire:

Agricultural occupation yes/no

Pesticide exposure yes/no

Proteinuria >15 mg/L

CKD defined as SCr ≥1.5 mg/dL among proteinuria positive subjects

For proteinuria:

OR agricultural work = 1.62 [0.75-3.49]

OR pesticide exposure = 0.79 [0.42-3.47]

For SCr ≥1.5: no associations with agricultural work or pesticide exposures

No association with agricultural work

No association with pesticide exposure

-------------

Cross-sectional; crude pesticide exposure assessment; possible confounding; possible selection bias in second phase

Explanation value: low

Torres-LaCourt et al., 2008 [88]

Nicaragua

Cross-sectional population-based survey

Random sample of 337 adults aged 20-60 (129 M, 208 F) from 2 rural communities

Questionnaire:

Current agricultural work yes/no

Mixing or applying pesticides yes/no

Previous pesticide intoxication yes/no

CKD stage 3 or higher (eGFR <60 ml/min/1.73m2)

Results reported separately for the two communities, analyses not adjusted for potential confounders:

ORs current agricultural work = 1.87 [0.88-3.99] and 2.68 [1.12-6.39]

ORs mixing/applying pesticides = 2.11 [0.99-4.50] and 4.80 [2.33-9.89]

ORs previous pesticide intoxication = 1.22 [0.32-4.67] and 1.19 [0.31-4.59]

Positive association with agricultural work

Positive association with pesticide exposure

No association with previous pesticide intoxication

-------------

Cross-sectional; crude exposure assessment; high risk for confounding

Explanation value: low

Sanoff et al., 2010 [89]

Nicaragua

Volunteer screening program with nested case-control analysis

Screening: 997 volunteers aged >18 y (848 M, 149 F)

Case-control: 334 M, 112 cases

Questionnaire:

Field labor yes/no

Work with or exposure to pesticides yes/no

eGFR

Screening: <60 vs ≥ 60 ml/min/1.73m2

Case control: <60 vs ≥ 80 ml/min/1.73m2

Screening:

OR agricultural field labor = 2.48 [1.59-3.89]

OR pesticides = 1.38 [0.90-2.11]

Case -control:

OR agricultural field labor = 2.38 [1.44-3.93]

OR pesticides = 1.57 [0.97-2.55]

Positive association for agricultural field labor

Weak positive association with pesticide exposure

-------------

Screening survey; crude exposure assessment; insufficient adjustment for potential confounders; likely selection bias

Explanation value: medium

O’Donnell et al., 2011 [90]

Nicaragua

Cross-sectional population-based survey; nested case-control analysis

Random sample of 771 individuals aged ≥18 (298 M, 473 F) from 300 eligible households

Case-control: 98 cases, 221 controls

Questionnaire:

Agricultural work yes/no

Pesticide exposure yes/no

Mixing or applying pesticides yes/no

CKD ≥ stage 3 (eGFR <60 ml/min/1.73m2)

Unadjusted/sex and age adjusted logistic regressions:

OR agricultural work = 2.09 [1.08-4.05]/1.00 [0.44-2.27])

OR any pesticide exposure = 2.45 [1.31 – 4.57]/1.85 [0.84, 4.07])

OR mixing or applying pesticides = 1.78 [1.09 – 2.91]/1.32 [0.66-2.64]

No association with agricultural work

Weak positive association with any pesticide exposure

No association with mixing or applying pesticides

-------------

Cross-sectional; crude exposure assessment; likely confounding; likely selection bias

Explanation value: medium

Orantes et al., 2011 [91]

El Salvador

Community screening and cross-sectional survey

775 individuals age ≥ 18, (343 M, 432 F)

Questionnaire:

Agricultural occupation yes/no

Contact with agrichemicals yes/no

CKD stages 1-5 (2 determinations with a 3-month interval)

OR agricultural occupation = 1.35 [0.63–2.88]

OR contact with agrichemicals = 1.23 [0.66 – 2.31]

No association for agricultural occupation

No association for contact with agrichemicals

-------------

Cross-sectional; crude exposure assessment; risk for confounding; incomplete strategy for statistical analyses

Explanation value: medium

Laux et al., 2012 [93]

Nicaragua

Community-based cross-sectional survey

267 adults (120 M, 147 F)

Questionnaire:

Work with pesticides yes/no

Proteinuria

OR work with pesticides = 1.09 [0.6–1.98]

No association with pesticide exposure

-------------

Cross-sectional; crude exposure assessment; study conducted in non-CKDu area

Explanation value: medium

Raines et al., 2014 [45]

Nicaragua

Cross-sectional population-based survey; nested case-control analysis

424 adults (166 M, 258 F)

280 in case-control analysis (78 cases)

Questionnaire:

Agricultural worker yes/no

Among subset of agricultural workers:

Lifetime days of:

-mixing pesticides

-applying pesticides

Self-reported history of accidentally inhaling pesticides

Degree of use of personal protective equipment (PPE)

eGFR <60 ml/min/1.73 m2

Case-control: <60 vs ≥ 90 ml/min/1.73 m2

OR agricultural worker 2.05 [0.61-6.90]

Subset agricultural workers:

Lifetime days of mixing and applying pesticides: p = 0.13 and p = 0.22 respectively

Level of PPE: p = 0.35

OR for accidental inhalation of pesticides = 3.14 [1.12 – 8.78]

Weak association with agricultural work

No association with main pesticide exposure indicators

No association with PPE

Accidental inhalation of pesticides associated with low eGFR, but pesticide inhalation without further specifications is not interpretable

-------------

Cross-sectional; unclear exposure indicators, possible confounding

Explanation value: medium

Laws et al., 2015 & Laws et al., 2016 [73, 74]

Nicaragua

Cohort

284 sugarcane workers (251 M, 33 F), incl. 29 agrichemical applicators

Job title: agrichemical applicator

eGFR (ml/min/1.73m2)

Biomarkers of early kidney injury NGAL, NAG, IL-18, albuminuria

Mean change eGFR for pesticide applicators during harvest season −3.8 (−9.9, 2.3)

Mean changes of early injury markers for pesticide applicators during harvest season:

NGAL −0.1 μg/g (p = 0.9)

NAG -0.12 μg/g (p = 0.6)

IL-18 -1.2 ng/g (p = 0.6)

ACR +0.3 mg/g (p = 0.8)

No association between a job of spraying pesticides with decrease in kidney function or increase in indicators of early tubular damage over one cutting season

-------------

Cohort design with short 6-month follow up; crude assessment with jobtitle for current exposure

Explanation value: medium

García-Trabanino et al., 2015 [94]

El Salvador

Cross-sectional occupational survey

189 sugarcane cutters (168 M, 21 F)

Questionnaire:

Pesticide use yes/no

Use of specific pesticides yes/no:

Herbicides: glyphosate, paraquat, 2,4-D, triazines

Insecticides: specific organophosphates, carbamates, pyrethroids

eGFR <60 ml/min/1.73 m2

Ever use of any pesticide not associated with low eGFR

Ever use of carbamate insecticides: 74% among workers with reduced eGFR vs 29% among remaining workers and a significant predictor in multivariate model

Association with ever use of carbamate insecticides

No association with other groups of pesticides

-------------

Cross-sectional; exposure assessment specific for chemical groups, but unquantified; multiple comparisons

Explanation value: medium

Wesseling et al., 2016 [99]

Nicaragua

Occupational cross-sectional study

86 sugarcane cutters, 56 construction workers, 52 subsistence farmers, all males

Questionnaire:

Pesticide use ever yes/no

Use of specific pesticides yes/no: glyphosate, paraquat, 2,4-D, chlorpyrifos, cypermethrin

eGFR <80 ml/min/1.73 m2

Ever use of any pesticide and ever use of specific pesticides not associated with reduced eGFR, for all workers combined and in analyses restricted to cane cutters

No association with ever use of pesticides

No association with any of the specific pesticides

-------------

Cross-sectional; exposure assessment specific for chemical groups, but unquantified

Explanation value: medium

  1. Abbreviations: CKD chronic kidney disease (u: of unknown etiology; nt: not related to traditional risk factors), eGFR estimated glomerular filtration rate, ESRD end-stage renal disease, F female, M male, OR odds ratio [95% confidence interval], SCr serum creatinine, NGAL neutrophil gelatinase-associated lipocalin, NAG N-acetyl-D-glucosaminidase, IL-18 interleukin-18, ACR urinary albumin-to-creatinine ratio
  2. aExplanation value: The study’s ability to contribute to knowledge about potential associations between pesticides and CKD or CKDu (according to the objective of the study), based on a qualitative evaluation of design and the validity of the results. For details see Additional file 2: Table S1 and the main text